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CAUPQRNIA 
Fiai-GAME 

"CONSERWOION  OF  WILD  UFB  THROUGH    EDUCATK^f 


f     Volume  34 

San  Francisco,  July,  1948 

Number  3       ■ 

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STATE  OF  CALIFORNIA 

DEPARTMENT  OF  NATURAL  RESOURCES 

DIVISION  OF  FISH  AND  GAME 
San  Francisco.  California 

EARL  WARREN 
Governor 

WARREN  T.  HANNUM 
Director  of  Natural  Resources 


nSH  AND  GAME  COMMISSION 

HARVEY  E.  HASTAIN,  President 
Brawley 
LEE  F.  PAYNE,  Commissioner  PAUL  DENNY,  Commissioner 

Los  Angeles  Etna 

EDWIN  L.  CARTY,  Commissioner  WILLIAM  J.  SILVA,  Commissioner 

Oxnard  Modesto 

E.  L.  MACAULAY 

Executive  Director 

San  Francisco 


CALIFORNIA  FISH  AND  GAME 

CARLTON  M.  HERMAN,  Editor Berkeley 

Editorial  Board 

RICHARD  S.  CROKER San  Francisco 

BRLA.N  CURTIS San  Francisco 

JOHN  E.  CHATTIN Berkeley 


California  Fiah  and  Game  is  a  publication  devoted  to  the  conservation  of  wildlife. 
It  is  published  quarterly  by  the  California  Division  of  Fish  and  Game.  All  material  for 
publication  should  be  sent  to  Dr.  Carlton  M.  Herman,  Editor,  Division  of  Fish  and 
Game,  Strawberry  Canyon,  University  of  California,  Berkeley  4,  California.  Manu- 
scripts should  be  typed,  double  spaced,  and  conform  to  the  style  of  previous  issues. 

The  articles  published  herein  are  not  copyrighted  and  may  be  reproduced  In  other 
periodicals,  provided  due  credit  is  given  the  author  and  the  California  Division  of  Fish 
and  Game. 

This  publication  is  sent  free  of  charge  to  interested  persons,  who  may  have  their 
names  placed  on  the  mailing  list  by  writing  to  the  editor.  Subscriptions  are  for  one 
year  and  must  be  renewed  annually.  A  postcard  will  be  included  with  each  October 
issue  for  renewal  of  subscriptions.  Subscribers  are  requested  to  notify  the  Division  of 
Fish  and  Game,  University  of  California,  Berkeley  4,  California,  of  changes  of  address, 
giving  old  address  as  well  as  the  new. 


"I 


California  Fish  and  Game 

"conservation  of  wildlife  through  education" 


Volume  34 


ISSUED  JULY  1,  19 4S 


No.  3 


TABLE  OF  CONTENTS 


Page 

T]u'  California  Sea  Lion  Census  for  1947 

P.  Bonnot  and  Wm.  E.  Ripley     89 

A  Contribution  to  the  Life  History  of  the  Sacramento  Perch 
{Archoplites  interruptus)  in  Clear  Lake,  Lake  County,  Cali- 
fornia   G.  I.  Murphy     93 

Notes  on  the  Biology  of  the  Sacramento  Hitch  {Lavinia  e.  exili- 

cauda)  of  Clear  Lake,  Lake  County,  California G.  I.  Murphy  101 

Kokanee  in  California B.  Curtis  and  J.  C.  Fraser  111 

Experiments  on  the  Management  of  Colorado  River  Beaver 

A.  L.  Hensley  and  B.  C.  Fox  115 

Notes — 

Some  New  and  Unusual  Fishes  from  Southern  California 

J.  E.  Fitch  133 

Hermaphroditism  in  Chinese  Ring-necked  Pheasant. 


.M.N.Rosen  135 


Resignation  of  Commission  President,  H.  H.  Arnold 136 

Appointment  of  Commissioner  E.  L.  Carty 136 

Resignation  of  Emil  J.  N.  Ott,  Jr.,  as  Executive  Officer 136 

Appointment  of  E.  L.  Macaulay  as  Executive  Officer 136 

Reports 137 


(87) 


THE  CALIFORNIA  SEA  LION  CENSUS  FOR  1947^ 

By  Paitl  Bonnot,  and  Wm.  Ellis  Ripley 

Bureau  of  Marine  Fisheries 

California  Division  of  Fish  and  Game 

At  the  beginning  of  the  last  century  great  herds  of  sea  lions  lived 
along  the  California  coast.  A  local  race  of  fur  seals,  and  a  species  of  sea 
elephants  inhabited  the  southern  half  of  the  coastal  area.  The  fur  of  the 
fur  seals  and  the  oil  from  the  sea  lions  and  sea  elephants  found  a  ready 
market.  The  seal  hunters  pursued  them  with  a  methodical  persistence 
that  practically  exterminated  the  fur  seals  and  sea  elephants,  and 
reduced  the  sea  lion  herds  so  drastically  that  it  was  no  longer  profitable 
to  hunt  them.  By  the  end  of  the  century  the  seal  hunters  had  moved  on 
to  greener  fields,  or  had  taken  up  commercial  fishing. 

In  the  last  20  years  commercial  fishing  along  the  California  coast 
has  grown  tremendously.  Canneries  and  reduction  plants  have  increased 
in  number  and  capacity.  Fishing  boats  and  gear  have  followed  suit. 
The  20-foot  boats,  that  landed  500  pounds  of  fish  taken  in  a  local  area, 
have  been  replaced  by  ocean-going  purse  seiners  that  deliver  200  tons. 


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Figure   25.     Steller  Sea  Lions,  Ann  Nuevo  Rookery.  Photograph  hv 
"Wm.  E.  Ripley,  .June  27,  194  7 

Because  of  recurring  complaints  of  damage  by  sea  lions,  a  number 
of  surveys  have  been  made  to  determine  the  size  of  the  population,  and 
to  determine,  if  possible,  what  the  animals  eat,  and  the  amount  of  damage 
they  actually  do. 

1  Submitted  for  publication  February,  1948.  We  take  pleasure  in  acknowledging 
our  indebtedness  to  the  officers  and  men  of  the  United  States  Navy,  Blimp  Squadron 
One,  based  at  Moffett  Field  and  Santa  Ana,  California,  for  the  cooperation  and  assist- 
ance given  us  in  making  this  survey. 


-89600 


(89) 


90  CALIFORNIA   FISH   AND    GAME 

Table  I  gives  the  population  for  the  years  in  which  surveys  have 
been  undertaken.  The  census  is  taken  during  June  or  July,  the  middle 
of  the  breeding  season,  at  which  time  the  animals  are  concentrated  on 
their  rookeries.  At  other  times  of  the  year  they  are  scattered  along  the 
entire  coast.  The  Steller  bulls  are  not  numerous  in  California  during  the 
winter.  They  appear  to  move  up  the  coast  to  British  Columbia  and 
southern  Alaska.  The  Californias  may  also  evince  a  northward  movement 
during  the  winter,  some  Lower  California  animals  migrating  to  southern 
California. 

Sea  lions  seem  to  have  a  more  catholic  taste  in  the  matter  of  diet 
than  most  carnivorous  animals.  They  eat  any  fish,  mollusc,  or  crustacean 
that  is  locally  plentiful  and  easily  caught.  At  times  they  are  a  definite 
nuisance  to  fishermen.  They  frighten  and  scatter  schools  of  fish,  and 
damage  nets  and  gear.  However  their  numbers,  their  consumption  of  fish 
and  the  damage  to  fishing  gear  attributed  to  them  are  usually  exagger- 
ated by  fishermen.  Despite  the  avowed  depredations  of  the  sea  lions,  the 
commercial  fisherman  of  California  manage  to  deliver,  in  an  average 
season,  over  a  billion  pounds  of  fish. 

During  the  last  two  seasons,  an  innovation  in  the  method  of  taking 
the  sea  lion  census  has  been  introduced  with  the  use  of  planes  and  blimps. 
This  technique  has  improved  the  accuracy  of  the  census.  Several  rookeries 
were  studied  and  photographed  which  previously  could  not  be  accurately 
estimated  as  it  was  not  possible  to  approach  them  either  from  the  land 
or  by  boat.  The  whole  coast  line  and  the  outlying  islands  can  be  examined 
in  two  or  three  days  instead  of  the  two  or  three  weeks  previously  required, 
and  comprehensive  photographs  can  be  more  readily  obtained.  On 
enlarged  photographs  it  is  possible  to  count  the  animals  accurately. 
It  has  been  found  that  estimates  of  the  number  of  animals,  by  experienced 
observers,  are  within  5  percent  of  the  numbers  actually  counted  on  the 
photographs. 

In  1946  the  census  was  compiled  from  the  counts  and  estimates  of 
a  number  of  individuals.  The  1946  report  employs  a  different  manner  of 
presentation  than  that  used  in  previous  reports,  and  is  therefore  not 
comparable  with  them.  The  totals  for  1946  are  given  at  the  bottom  of 
Table  I.  The  1989  report  is  based  on  estimates  made  in  March,  and 
includes  only  about  half  the  rookeries  (Fry,  1939).  It  cannot  therefore 
be  logically  compared  with  other  seasons. 

In  1947  two  experienced  observers  surveyed  the  entire  coast  line. 
Due  to  unavoidable  mishaps,  photographs  of  some  five  rookeries  were 
unsatisfactory,  or  were  not  obtained ;  but  all  rookeries,  with  the  excep- 
tion of  San  Nicolas  Island,  which  was  checked  by  the  crew  of  a  boat  of 
the  Bureau  of  Patrol,  were  observed.  Where  satisfactory  photographs 
were  obtained,  the  estimates  check  within  5  percent ;  so  it  may  be  assumed 
that  the  estimates  not  verified  by  photographic  counts  will  be  within 
that  tolerance. 

The  total  population  of  both  species  of  sea  lions  on  the  California 
coast  in  1947  was  found  to  be  8,716. 

In  the  last  20  years  the  sea  lion  population  has  remained  fairly  stable. 
The  average  for  the  five  previous  surveys  is  a  little  over  7,000.  The 
increase  in  1947  may  be  the  result  of  the  more  rapid  and  comprehensive 
coverage  of  the  coast  by  air.  which  permits  the  detection  and  inclusion 
of  individuals  and  small  groups  in  out-of-the-way  and  isolated  parts  of 
the  coast. 


SEA    LIOX    CENSUS 


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92  CALIFORNIA   FISH   AND    GAME 

References 

Bonnot,  Paul 

1928.     Report  on  the  Seals  and  Sea  Lions  of  California.  Fish  Bulletin  No.  14, 
p.  61,  fig.  38. 

1931.     The   California    Sea   Lion   Census   for   1930.    California   Fish    and   Game, 
Vol.  17,  pp.  150-155. 

1937.  California  Sea  Lion  Census  for  1936.  California  Fish  and  Game,  Vol.  23, 
pp.  108-112. 

Bonnot,  Paul :  Clark,  G.  H. :  Hatton,  S.  Ross 

1938.  California  Sea  Lion  Census  for  1938.  California  Fish  and  Game,  Vol.  24, 
pp.  415-419. 

Bureau  of  Marine  Fisheries 

1947.     California  Sea  Lion  Census  for  1946.  California  Fish  and  Game,  Vol.  33, 
pp.  19-22. 

Fry,  D.  H.,  Jr. 

1939.  A  AVinter  Influx  of  Sea  Lions  from  Lower  California.  California  Fish  and 
Game,  Vol.  25,  pp.  245-250. 


A  CONTRIBUTION  TO  THE  LIFE  HISTORY  OF  THE 

SACRAMENTO  PERCH  (ARCHOPLITES  HVrER- 

RUPTUS)  IN  CLEAR  LAKE,  LAKE 

COUNTY,  CALIFORNIA^ 

By  Gabth  I.  Murphy 

Bureau  of  Fish  Conservation 

California  Division  of  Fish  and  Game 

Introduction 

In  the  course  of  investigations  on  Clear  Lake  a  limited  amount  of 
data  relative  to  the  Sacramento  Perch  (Archoplites  interruptus)  was 
obtained.  Since  little  information  is  available  on  this  centrarchid,  the  only 
native  member  of  the  sunfish  family  west  of  the  Rockies,  it  is  believed  that 
any  observation  is  a  contribution. 

Clear  Lake  is  a  large  lowland  lake  of  40,000  surface  acres,  located 
in  the  Upper  Sonoran  Life  Zone  of  central  Northern  California.  It  is  a 
part  of  the  Sacramento-San  Joaquin  drainage  basin,  being  connected  hy 
its  outlet.  Cache  Creek,  with  the  Sacramento  River  via  the  Yolo  By-pass. 

The  Sacramento  Perch  is  restricted  to  the  Sacramento-San  Joaquin 
drainage  and  the  smaller  neighboring  Pajaro  River  system.  Before  the 
introduction  of  alien  species,  the  Sacramento  Perch  was  exceedingly 
abundant  throughout  the  lowland  areas.  Its  size  was  reported  by  Jordan 
and  Evermann  (1896-1900)  as  12  to  24  inches.  At  the  present  time  it  is 
scarce  except  in  isolated  localities,  one  of  which  is  Clear  Lake. 

General  Information 

The  Sacramento  Perch  (Fig.  26)  occupies  a  minor  position  in  the 
sport  catch  of  Clear  Lake.  In  1947,  it  constituted  1  percent  of  the  total 
catch.  Formerly,  trout  and  the  Sacramento  Perch  were  the  only  game 
fish  to  be  found  in  the  lake.  Since  then  introduced  sunfish,  bass,  and  cat- 
fish, and  changing  ecological  conditions,  have  reduced  the  numbers 
of  this  species.  In  1947  the  catch  of  Sacramento  Perch  was  made  in  April, 
May,  and  June  only,  a  period  that  corresponds  roughly  with  prespawning 
and  spa^vning  concentrations.  The  only  explanation  for  their  disappear- 
ance after  this  date  is  that  they  must  range  the  entire  lake  after  spawn- 
ing. Since  their  numbers  are  small,  the  chances  of  their  being  captured 
by  offshore  anglers  are  small. 

No  studies  of  the  food  habits  of  the  Sacramento  Perch  were  made. 
However,  b,y  inference,  a  rough  pattern  emerges.  Young  of  the  year  are 
found  in  association  with  bluegill  (Lepomis  macrocliirus)  in  the  littoral 
zone,  where  they  probably  feed  on  larger  zooplanktons  and  insects. 
Adults  are  captured  on  spinners  and  live  minnows,  but  almost  never  on 
worms,  so  it  can  be  assumed  that  after  reaching  a  certain  size  they  become 
at  least  partially  piscivorous.  Lindquist,  Deonier,  and  Hancey  (1943) 

1  Submitted  for  publication  March,  1948. 

(93) 


94 


CALIFORNIA   FISH    AND    GAME 


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SACRAMENTO  PERCH  95 

found  the  specimens  they  examined  had  fed  on  all  stages  of  the  phantom 
midge  (Chaohorus  astictopusj,  which  is  distributed  over  most  of  the  off- 
shore section  of  Clear  Lake.  The  young  of  the  native  cyprinids,  such  as 
the  Sacramento  Hitch  (Lavinia  e.  exilicauda)  move  into  the  oif  shore  areas 
during  the  middle  of  the  summer,  affording  a  supply  of  forage  fish  to  the 
perch. 

Spawning  Habits 

A  school  of  spawning  Sacramento  Perch  was  observed  on  June  15, 
1947,  off  Austins  Pier  near  Lower  Lake.  No  spawning  fish  were  in  the 
area  on  June  14th  and  none  on  June  16th.  According  to  the  boatman,  Mr. 
Jess  Loomis,  spaw^ling  activity  commenced  about  9  a.m.  on  June  15th. 
The  writer  began  observations  at  12  noon. 

An  estimated  50  adult  fish  were  spawning  in  an  area  12  feet  long 
and  four  feet  wide.  The  spawning  ground  ad  jointed  a  rock  breakwater. 
The  water  depth  varied  from  one  to  two  feet  and  the  temperature  was 
75.5  degrees  Fahrenheit.  The  substrate  consisted  of  boulders  from  three 
inches  to  one  foot  in  diameter,  covered  by  a  hea-vy  gro's\i;h  of  algae.  A 
few  straggly  growths  of  pond  weed,  Potamogeton,  occurred  in  the  area. 
As  seen  from  above,  the  fish  were  paired,  although  some  exchange  of 
mates  appeared  to  take  place.  The  spawning  activity  of  each  pair  was 
roughly  cyclic.  Activity  would  commence  by  general  restlessness  of  the 
pair,  accompanied  by  considerbale  nudging  and  butting.  Egg  deposition 
followed  and  was  accomplished  in  a  few  seconds  with  the  vents  in  close 
approximation.  During  deposition  both  fish  were  tense,  the  female  with 
mouth  agape,  and  both  fish  often  in  a  vertical  position,  with  either  the 
heads  or  the  tails  up.  Deposition  was  followed  by  more  predeposition 
activity,  more  deposition,  and  finalh^  by  a  rest  period  of  about  five  min- 
utes, during  which  any  intruder  was  ejected  from  the  pair's  deposition 
area.  During  the  rest  period  the  female  would  occasionally  stray  from 
the  deposition  area  while  the  male  remained  on  guard.  (The  term  "depo- 
sition area"  is  used,  since  each  pair  spawned  in  a  definite  area  about  1.5 
feet  in  diameter,  although  no  nest-building  activity  of  any  sort  was 
observed.) 

By  3  p.m.  activity  on  the  spawning  ground  had  decreased  markedly 
and  comparatively  few  fish  were  in  sight.  Most  of  these  were  males  guard- 
ing the  deposition  area.  B}^  4  p.m.  all  fish  had  left  the  spawning  ground. 

Examination  of  the  substrate  showed  that  the  adhesive  eggs  were 
attached  directly  to  the  heavy  growth  of  algae  on  the  rocks  (Figure  27). 
A  few  were  found  on  the  Potamogeton  and  a  few  on  bare  rock.  The 
vertical  position  assumed  occasionally  by  the  spawning  fish  may  have 
been  due  to  deposition  on  a  vertical  surface ;  considerable  spawn  was 
found  on  vertical  surfaces,  but  it  was  impossible  to  tell  if  it  was  deposited 
while  in  the  vertical  position. 

An  abundance  of  the  types  of  substrate  on  which  most  eentrarchids 
spa%vn,  such  as  gravels,  existed  nearby,  but  no  Sacramento  Perch  were 
observed  using  them.  The  use  of  algae-covered  rocks  and  plants  as  a  sub- 
strate was  one  of  choice. 

During  the  height  of  spawning  activity,  it  was  almost  impossible  to 
disturb  the  fish.  As  the  activity  subsided,  the  females  were  the  first  to 
wander  off.  The  males  remained  in  the  deposition  areas  for  a  short  time, 
up  to  30  minutes,  apparently  on  the  possibility  of  additional  females 


96 


CALIFORNIA   FISH    AND    GAME 


appearing,  and  then  wandered  off.  During  the  late  afternoon,  after 
spawning  had  subsided  considerably,  the  fish  were  very  skittish,  males 
and  females  leaving  the  area  permanently  at  the  slightest  provocation. 
By  4  p.m.  no  fish  were  observed  on  the  spawning  ground. 

On  June  15th  eggs  were  extremely  abundant  on  the  algae-covered 
rocks,  in  some  cases  forming  a  solid  crust.  On  June  16th  it  was  almost 
impossible  to  locate  eggs.  The  few  that  were  found  were  well  along  in 
development,  with  hearts  beating,  indicating  that  development  is  rapid, 
as  in  other  centrarchids. 

A  female  10.5  inches  long  snagged  off  the  spawning  bed  contained 
an  estimated  84,000  unspawned  mature  eggs. 

The  first  Sacramento  Perch  of  the  year  were  taken  in  Clear  Lake  on 
June  9,  1947,  at  an  average  length  of  0.8  of  an  inch,  w^hich  indicates  that 
spawning  had  begun  in  May.  By  June  24th  the  majority  had  spawned, 
judging  by  the  condition  of  the  gonads  of  adults  captured  in  nets.  Dur- 
ing the  period  May  19th  to  June  26th  the  water  temperatures  of  Clear 
Lake  at  a  depth  of  two  feet  varied  from  a  maximum  of  84  degrees  F.  to  a 


Figure  27.     Length-weight   relationship    of    Sacramento    Perch,    Clear   Lake, 

1946-1947.  Curve  fitted  by  eye. 


SACRAMENTO   PERCH 


97 


minimum  of  62  degrees  F.,  as  recorded  from  a  maximum-minimum  ther- 
mometer. 

Sacramento  Perch  in  Clear  Lake  spawn  after  their  first  year,  judg- 
ing by  the  samples  collected. 

Growth 

It  appears  that  after  the  young  of  the  year  reach  a  length  of  about 
two  inches  they  abandon  the  immediate  shoreline  and  range  the  open 
waters  of  the  lake.  Seine  hauls  on  July  7th  and  August  7th  took  speci- 
mens 1.9  and  2.0  inches  long  respectively  near  shore.  The  length  of  the 
individuals  in  the  shore  population  remains  relatively  constant,  since 
the  larger  individuals  move  out  of  reach  of  small  seines.  The  largest  fish 
of  the  year  taken  in  1947  was  3.5  inches  long,  and  was  captured  on 
October  11th  in  a  iyke  net  set  120  yards  off  shore. 

Figure  27  gives  the  length-weight  relationship  of  Sacramento  Perch 
in  Clear  Lake. 


? — ? — (p    'I    n 


0/5  10  /S  10  15 

Figure  28.     Growth  rate  of  Sacramento  Perch,  Clear  Lake,  1946-1947. 

The  graph  (Fig.  28)  is  based  on  59  scale  samples  taken  in  1946  and 
1947.  Some  difficulty  was  experienced  in  reading  the  scales,  as  the  species 
apparently  forms  ' '  false  checks ' '  quite  readily.  These  checks  may  or  may 
not  be  spawning  marks.  In  all  cases  the  first  annulus  was  readily  located 
(Fig.  29). 


3—89600 


98 


CALIFORNIA   FISH    AND    GAME 


Figure  29.     Typical   scale   of   a   female    Sacramento   Perch,    20.0    centimeters    (8 
inches)   in  length  taken  April  27,  1947.  This  fish  is  in  Age  Class  2. 

Discussion 

The  spawning  habits  of  the  Sacramento  Perch  are  unique  among 
the  family  Centrarchidae.  Breder  (1936)  gives  a  comprehensive  review 
of  the  family's  spawning  habits.  Of  the  25  species  recognized  at  that  time, 
data  for  20  indicated  that  the  breeding  habits  of  this  group  are  remark- 
ably uniform.  The  data  given  below  are  taken  from  page  40  of  Breder 's 
paper. 

REPRODUCTIVE  HABITS  OF  CENTRARCHIDAE 

Attribute  Manifestation 

"1.  Sex  recognition  Differential  behavior. 

*2.  Spawning  position     Pair  headed  the  same  way  with  their  ventral  surfaces  in  con- 
tact, the  female  reclined  on  one  side. 
In  a  depression  in  sand  or  gravel  made  by  the  male. 
Moderately  adhesive,  attached  to  gravel  and  each  other. 
Not  essential  for  respiration  of  the  eggs.  A  protection  from 

silting  and  enemies  only. 
Male  alone  incubates   and  guards.   Female   normally   leaves 

when  eggs  are  laid. 
Chiefly   the   pectoral   fins   aided   by   the   anal,   or   swimming 

motions  of  the  whole  body. 
Guarded  in  nest  by  male  until  ready  to  swim  or  later. 


3.  Location  of  nest 
•4.  Nature  of  eggs 
5.  Need  for  aeration 


6. 


8. 


Roles  of  parents 
Incubating  method 
Care  of  young 


Of  these  eight  generalized  attributes  of  the  family  Centrarchidae, 
only  three  (marked  with  an  asterisk  above)  were  observed  in  the  Sac- 
ramento Perch.  A  fourth,  territoriality,  only  implied  in  the  above  tabu- 
lation, is  present  during  spawning  only.  The  spawning  pattern  of  this 


SACRAMENTO   PERCH  99 

species  appears  to  be  primitive.  The  absence  of  any  nest  building  activity, 
despite  a  choice  of  site,  and  the  absence  or  virtual  absence  of  any  sort 
of  parental  care  ^  form  a  basic  pattern  on  which  the  more  specialized 
breeding  behaviors  of  other  centrarchids  could  be  developed. 

The  schooling  behavior  of  Sacramento  Perch  at  spawning  time  is 
unique.  Breder  (1936)  describes  the  tendency  of  many  sunfishes  to  school 
prior  to  spawning.  On  moving  into  shallow  water,  these  schools  break 
up,  and  any  aggregation  into  colonies  Breder  ascribes  to  limitation  of 
suitable  spawning  sites.  Sacramento  Perch  also  school  in  the  pre-spawn- 
ing  period,  as  evidenced  by  the  fact  that  an  angler  on  capturing  one 
perch  can  generally  take  large  numbers  in  the  same  locality.  Unlike  other 
centrarchids,  they  retain  the  schooling  habit  during  the  actual  spawning. 
In  addition  to  the  school  observed  by  the  writer,  various  lay  observers 
have  reported  large  aggregations  of  spawning  perch.  After  spawning  the 
schools  break  up  and  the  fish  depart  singly.  This  failure  of  the  schools  to 
break  up  until  after  spawning  is  probably  a  primitive  characteristic  and 
may  be  associated  with  weak  sex  recognition  characters  and  behavior. 
It  is,  of  course,  possible  to  interpret  the  spawning  pattern  as  degenerate. 
Archoplites  is  a  survivor  of  an  ancient  fauna  which  probably  antedated 
the  barrier  of  the  Rocky  Mountains  (Miller  1946) .  Thus,  it  is  not  surpris- 
ing that  its  reproductive  habits  are  generalized. 

It  is  quite  probable  that  the  scarcity  of  Sacramento  Perch  is  due  to 
its  failure  to  guard  its  eggs.  In  aboriginal  times  there  were  comparatively 
few  species  in  the  Sacramento-San  Joaquin  system  which  were  likely  to 
eat  unprotected,  exposed,  fish  eggs.  Since  that  time  black  bass,  crappie, 
bluegill,  carp,  and  catfish  have  been  introduced  into  California.  Neale 
(1931)  demonstrated  to  his  satisfaction  that  of  these  the  bluegill,  carp, 
and  catfish  (Ameiurus  nehulosus  or  Idalurus  catus)  would  eat  eggs  of 
spawning  fish.  According  to  his  observations,  the  Sacramento  Perch 
"spawns  among  aquatic  growth,"  and  does  not  build  nests  as  do  other 
centrachids.  This  is  in  general  agreement  with  the  data  presented  above. 
With  the  introduction  of  the  species  listed  above,  the  Sacramento  Perch 
was  no  longer  living  in  the  isolation  which  it  had  enjoyed  since  the 
Pliocene  period.  It  became  subjected  to  attack  at  its  weakest  point,  its 
unguarded  eggs,  until  today  it  is  only  occasionally  taken  by  the  angler. 
Of  the  myriads  of  eggs  which  were  deposited  on  June  15th,  only  a  few 
could  be  found  on  June  16th,  and  none  on  subsequent  days.  The  locality 
in  which  they  were  spawned  was  swarming  with  Bluegill  one  to  two 
inches  long,  which  probably  consumed  the  eggs. 

An  interesting  case  is  that  of  Thurston  Lake,  located  near  Clear 
Lake.  In  this  lake  Sacramento  Perch  coexisted  successfully  with  the 
Brown  Bullhead  (Atneiurus  nehulosus)  and  the  Largemouth  Black  Bass 
{Micropterus  salmoides).  In  1933  White  Catfish  {Idalurus  catus)  were 
introduced,  and  shortly  afterwards  the  Sacramento  Perch  disappeared 
completely. 

Curtis  (1946)  experimented  with  16  adult  Sacramento  Perch  and 
30  adult  Green  Sunfish  {Lepomis  cyanellus)  which  were  placed  in  a  one- 
third  acre  pond  at  Elk  Grove,  California,  on  March  19,  1946.  When  the 
pond  was  drained  on  August  9,  23,000  young  Sacramento  Perch  and 
1,500  young  Green  Sunfish  were  recovered.  The  success  of  the  Sacra- 

1  Some  tendency  to  stay  near  the  incubating  eggs  has  been  reported  for  Sacra- 
mento Perch  in  very  small  waters  (artificial  ponds,  etc.).  No  such  tendency  was  seen 
here. 


100  CALIFORNIA   FISH   AND   GAME 

mento  Perch  was  probably  due  to  their  greater  fecundity  and  to  the 
probability  that  they  completed  spawning  before  the  Green  Sunfish  of 
the  year  were  large  enough  to  consume  eggs,  if  they  attack  eggs  at  all. 
The  30  adult  sunfish  (average  weight  7.5  ounces)  would  be  unlikely  to 
make  serious  inroads  into  the  perch  eggs,  partly  because  of  the  small 
number  in  a  one-third  acre  pond,  partly  because  they  may  have  been 
involved  in  spawning  of  their  own,  and  possiblj^  because  adult  Green 
Sunfish  may  not  disturb  eggs,  particularly  if  other  food  is  abundant. 
Similar  experiments  using  Largemouth  Black  Bass,  Bluegill,  and  Brown 
Bullhead  resulted  in  a  predominance  of  Sacramento  Perch. 

Summary 

The  Sacramento  Perch,  a  holdover  from  an  ancient  fauna,  is 
restricted  to  the  Sacramento-San  Joaquin  and  allied  drainages.  At  the 
present  time  its  numbers  are  greatly  reduced.  Its  feeding  habits  are 
insectivorous  and  piscivorous. 

Spawning  habits  are  probably  primitive.  The  schooling  tendency  is 
retained ;  nest  building  absent ;  and  guarding  manifested  only  by  terri- 
toriality during  spawning.  The  reduction  of  the  Sacramento  Perch  popu- 
lation probably  resulted  from  the  introduction  of  species  which  prey  on 
its  unguarded  eggs. 

Recommendations 

The  Sacramento  Perch  is  gravel}^  threatened  by  man 's  introduction 
of  alien  species  into  is  habitat.  It  is  not  only  a  zoological  rarity,  but  also 
a  worthwhile  game  fish.  It  is  desirable  that  further  studies  be  made  to 
explain  more  clearly  its  decline,  and  that  steps  be  taken  to  preserve  the 
species  in  limited  areas.  Experiments  to  determine  its  value  in  pond  fish 
culture  have  been  initiated  by  the  California  Division  of  Fish  and  Game, 
and  should  be  continued. 

References 

Bredor,  C.  M.,  Jr. 

1936.     The  Reproductive  Habits  of  North  American  Sunfishes  (Family     Centrar- 
chidae).     Zoologica,  Vol.  XXI,  No.  1,  pp.  1-48,  pis.  I-VII. 

Curtis,  B. 

1046.     Unpublished  data. 

.Jordan,  D.  S.,  and  B.  W.  Evermann 

],S!»6-1900.     The  Fishes  of  Middle  and  North  America.  U.  S.  Nat.  Mus.,  Bull.  47, 
pp.  1-3313,  pis.  I-CCCXCII. 

Lindquist,  A.  W.,  C.  C.  Deonier,  and  J.  E.  Hancey 

1943.     The  Relationship  of  Fish  to  the  Clear  Lake  Gnat  in  Clear  Lake,  California. 
California  Fish  and  Game,  Vol.  29,  No.  4,  pp.  196-202. 

Miller,  R.  11. 

1946.     The  Need  for  Ichthyological  Surveys  of  the  Major  Rivers  of  Western  North 
America.  Science,  Vol.  104,  No.  2710,  pp.  517-519. 

Neale,  G. 

1931.     Sacramento  Perch.     California  Fish  and  Game,  Vol.  17,  No.  4,  pp.  409-411. 


NOTES  ON  THE  BIOLOGY  OF  THE  SACRAMENTO 

HITCH  (LAVINIA  E.  EXILICAUDA)  OF  CLEAR 

LAKE,  LAKE  COUNTY,  CALIFORNIA^ 

By  Gaeth  I.  Murphy 

Bureau  of  Fish  Conservation 

California  Division  of  Fish  and  Game 

Introduction 

The  hitch  (Figure  30)  is  a  member  of  the  carp  family  (Cyprinidae). 
The  vernacular  name  ''hitch"  is  of  Indian  origin.  The  Pomo  tribes  living 
on  the  north  and  west  sides  of  Clear  Lake  apply  this  name  to  it,  but  those 
living  on  the  east  and  south  shores  call  it  "Chi."  The  genus  Lavinia 
is  represented  by  a  single  species,  indigenous  to  the  Sacramento-San 
Joaquin  drainage  basin  and  several  minor  but  related  drainages.  Con- 
siderable material  on  its  distribution  and  svstematics  is  to  be  found  in 
Rutter  (1903),  Snyder  (1913),  and  Miller  (1945). 


Figure  30.     Male  hitch,  6.7  inches  long,  captured  at  Scotts  Creek,  April  18,  1947 

The  data  presented  in  this  paper  were  derived  from  collections  and 
observations  made  at  Clear  Lake  and  its  tributary  streams  during  1946 
and  1947  and  from  observations  made  by  Shapovalov  in  1940.  Clear  Lake 
is  a  large,  lowland  lake  in  central  California  containing  a  typical  Cali- 
fornia warm-water  assemblage  of  fishes.  Its  surface  area  is  approximately 
40,000  acres. 

All  measurements  of  fish  were  made  to  the  nearest  millimeter,  using 
"fork  length."  Weights  were  taken  with  a  spring  balance  reading  to  the 
nearest  25  grams.  Scale  samples  were  taken  from  the  side  of  the  fish,  above 
the  lateral  line  and  below  the  dorsal  fin. 

General  Ecology  of  the  Hitch 

Through  its  range  as  a  whole  the  hitch  inhabits  lowland  areas  typi- 
fied by  sluggish  streams  and  sloughs.  Although  frequently'  it  lives  in  lakes 
and  ponds,  it  apparently  requires  gravel-bottomed  streams  for  successful 

1  Submitted  for  publication  March,  1948.  All  photographs,  except  Fig.  32,  by  the 
author. 

(  101  ) 


102  CALIFORNIA   FISH    AND   GAME 

spawning.  In  this  respect  its  life  cycle  is  comparable  to  that  of  the  rain- 
bow trout. 

The  importance  of  the  hitch  to  the  sport  fishery  is  its  value  as  forage 
for  the  spiny-rayed  game  fishes.  A  forage  fish  for  these  species  should 
have  certain  characteristics.  It  should  be  prolific.  It  should  be  innocuous 
in  its  feeding  habits.  It  should  be  available.  And  its  size  should  be  such 
that  it  remains  in  the  forage  fish  classification  for  at  least  one  year.  In 
general,  the  hitch  fits  these  specifications,  but  the  need  for  adequate 
spawning  streams  limits  its  use.  On  the  other  hand,  its  mandatory  stream 
spa^yning  and  weak  swimming  characteristic  make  it  a  forage  fish  that 
can  be  readily  controlled  when  the  need  arises. 

Feeding  Habits 

No  extensive  study  of  the  feeding  habits  of  the  hitch  was  made  by 
the  writer.  Lindquist,  Deonier,  and  Plancey  (1943),  found  young  hitch 
up  to  two  or  three  inches  long  in  the  lake  to  be  feeding  on  the  eggs,  larvae, 
and  adults  of  the  phantom  midge  (Chaohorvs  asHctopus),  commonly 
known  as  the  Clear  Lake  gnat ;  and  the  adult  hitch  feeding  on  plankton 
exclusively.  The  stomachs  of  several  small  hitch  examined  by  the  writer 
contained  larger  plankton  Crustacea  exclusively.  Five  stomachs  from 
adult  hitch  captured  by  gill  net  in  Clear  Lake  during  1946  contained 
only  plankton,  but  during  the  early  spring  an  adult  hitch  is  occasionally 
taken  by  an  angler  using  flies  or  worms  on  a  small  hook,  which  indicates 
the  insectivorous  habit  is  not  completely  abandoned  in  the  adult.  These 
scattered  data  indicate  that  the  hitch  while  young  (two  or  three  inches) 
feeds  on  smaller  insects  and  plankton,  and  during  its  adult  life  feeds 
very  largely  on  plankton. 

Spawning  Habits  and  Larval  Development 

The  hitch  is  very  prolific ;  a  10-inch  female  taken  in  March,  1947, 
contained  an  estimated  112,000  maturing  eggs.  This  great  fecundity 
is  probably  an  adaptation  to  offset  reproductive  hazards,  which  are 
numerous. 

During  late  March  and  early  April,  after  freshets  caused  by  late 
spring  rains,  the  hitch  move  out  of  Clear  Lake  into  the  tributary  streams 
to  spawn,  running  a  few  miles  upstream,  but  not  penetrating  the  more 
precipitous  reaches  of  the  streams.  Figure  31  illustrates  a  typical  reach 
of  hitch  spawning  water.  The  gradient  is  slight.  Most  of  the  streams  tribu- 
tary to  Clear  Lake  are  of  slight  gradient  in  the  lower  few  miles  and  are 
covered  with  gravel  and  rubble  up  to  five  inches  in  diameter.  In  the  past, 
enormous  numbers  of  hitch  moved  into  the  streams  after  the  late  rains. 
In  fact,  the  last  sizeable  rain  of  the  season  is  called  the  "hitch  rain"  by 
many  local  residents.  Of  recent  years  the  runs  have  been  small  or  non- 
existent. 

Shapovalov  (1940)  observed  spawning  hitch  in  Middle  and  Clover 
Creeks,  both  tributary  to  Clear  Lake  via  Scotts  Creek,  on  April  13,  1940. 
The  following  account  of  spa^vning  activity  is  taken  directly  from  his 
notes. 

' '  Spawning  was  taking  place  in  shallow  areas,  where  the  water  was 
three  to  five  inches  deep,  in  moderately  swift  water.  It  was  taking  place 
mostly  over  fine  to  medium  gravel,  on  even  riffles.  At  this  point  the  stream 


SACRAMENTO    HITCH 


103 


is  willow-liued.  Spawning  was  in  progress  at  this  location  at  10  a.m.,  when 
observations  were  first  made. 


r-  r- 


-r^-^-- 


>r  SS*^-"^^-^  *5.3  it^  .*^j 

3«pJ^.~i^JP" J  i^-^     f"  '-■'V.  '* 


r-^x 


Jk.,^^. 


5i*«S-'     .  v.-—     ^•?^-  -w^ 


Figure  31.     Hitch  spawning  in  Middle  Creels  at  bridge  on  Lakeport-Upper  Lake 
Road,  Lake  County,  April  13,  1940.  Photograph  by  Leo  Shapovalov 

"Spawning  was  also  going  on  at  the  same  time  in  Middle  Creek  at 
the  State  Highway  29  crossing  (on  the  Upper  Lake-Lakeport  Highway). 
At  10.30  a.m.  the  temperatures  in  degrees  Fahrenheit  in  Middle  Creek  at 
the  above  bridge  were  air  67.5  degrees,  water  58.5  degrees.  The  weather 
was  clear.  The  water  was  slightly  murky.  The  flow  of  the  stream  was  esti- 
mated to  be  75  second-feet  or  more.  The  average  width  was  about  35  feet 
and  the  average  depth  about  10  inches. 

"Observations  were  continued  only  until  11.30  a.m.,  at  which  time 
spawning  was  still  going  on  at  the  above  bridge  over  Middle  Creek.  Tem- 
peratures had  then  risen  to  air  73  degrees,  water  61.5  degrees. 

"In  spawning,  the  males  kept  close  to  and  slightly  behind  the 
females,  with  their  snouts  near  the  vents  of  the  females.  Often  four  and 
five  or  more  males  attended  one  female,  crowding  over  and  next  to  one 
another.  However,  they  were  not  observed  fighting. 

"The  deposited  eggs  were  not  covered  by  the  fish.  On  the  day  of 
observation  the  stream  flow  was  receding,  and  as  a  result  many  thousands 
of  eggs  were  exposed  on  gravel  bars.  Under  such  conditions,  mortality 
among  newly  laid  eggs  must  be  tremendous." 

The  run  of  fish  studied  by  the  writer  entered  Scotts  Creek  on  April 
17,  1947,  and  remained  in  the  stream  until  April  26th.  Roily  waters  at 
the  time  of  the  run  prevented  direct  observation  of  the  spawning  fish. 
Most  of  the  observations  were  made  at  a  riffle  just  below  the  mouth  of 
Middle  Creek. 

Figure  32  illustrates  the  composition  of  the  spawning  run  observed 
in  Scotts  Creek.  It  shows  that  while  the  males  become  mature  at  the  end 


104 


CALIFORNIA    FISH    AND    GAME 


of  their  first  year,  females  usually  do  not  mature  until  the  end  of  their 
third  year  of  life,  although  a  spawning  female  of  age  class  1  was  collected 
by  Shapovalov  in  March  of  1940. 


0 


Male 

Female. 

SBH 

10 


5  0  5 

Number  of  Spec/mens 


10 


Figure  32.  Age  Composition  of  Spawning  Hitcli,  Scotts  Creek,  Lake  County, 
April,  1947.  (Age  Class  0  includes  all  fish  that  have  not  completed  their  first  year  of 
life,  etc.) 

In  Scotts  Creek  eggs  could  not  be  recovered  from  the  pools  above  and 
below  the  riffle  but  could  be  recovered  from  the  riffle  b}^  a  technique  similar 
to  stream  bottom  sampling,  so  it  is  assumed  that  deposition  took  place  only 
in  riffle  areas.  Since  the  eggs  are  nonadhesive  and  sink  rapidly,  they  lodge 
in  spaces  in  the  gravel,  which  offer  some  protection  during  development. 
At  the  time  the  spawning  was  observed  the  flow  over  the  riffle  studied  was 
80.2  second-feet.  The  current  speed  over  the  riffle  varied  from  one-quarter 
foot  per  second  to  4f  feet  per  second  as  measured  by  a  current  meter. 


FiGURK  .33.  Hitch  Eggs.  The  small  egg  was  preserved 
immediately  after  extrusion,  and  the  larger  eggs  30  minutes 
after  extrusion. 


SACRAMENTO    HITCH  105 

Eggs  were  recovered  from  and  spawning  hitch  captured  on  the  sections  of 
the  riffle  having  a  speed  of  seven-eighths  foot  per  second  to  2^  feet  per 
second,  indicating  that  the  spawning  fish  have  definite  current  prefer- 
ences. The  eggs  were  A'ery  abundant  in  the  gravel,  their  numbers  ranging 
from  110  to  561  per  square  foot  on  May  8, 1947. 

Shortly  after  extrusion  the  egg  absorbs  water  and  a  liquid  cushion  is 
formed  between  the  membrane  and  the  yolk.  The  entire  process  takes 
about  30  minutes,  but  starts  almost  immediately.  This  necessitates  rapid 
fertilization.  Figure  33  shows  the  hitch  egg  before  and  after  this  process. 
The  smaller  egg  was  preserved  immediately  after  extrusion  and  the  larger 
eggs  30  minutes  after  extrusion. 

An  attempt  was  made  to  rear  a  batch  of  eggs.  They  were  artificially 
spawned  and  fertilized  and  placed  in  a  tray  through  which  tap  water  at 
62  degrees  F.  was  run.  The  longest  period  of  time  the  eggs  survived  was 
five  days.  In  three  days  the  surviving  embryos  were  moving  vigorously. 
On  the  fifth  day  the  hearts  were  beating.  On  the  basis  of  available  evi- 
dence, it  can  be  postulated  that  embryonic  development  takes  about  ten 
days  at  62  degrees  F.  and  that  the  larvae  become  free-swimming  in 
approximately  twenty  days. 

Failure  of  hitch  spawning  is  readily  possible.  Apparently  a  heavy 
rain  during  late  ]\Iarch  or  April  is  needed  to  bring  the  adults  into  the 
streams.  During  1946  virtually  no  hitch  from  Clear  Lake  spawned. 
Streamside  residents  report  that  no  fish  ran.  Hitch  of  the  year  were  quite 
scarce  and  adult  hitch  captured  during  the  summer  were  eggbound.  This 
is  thought  to  be  due  to  a  lack  of  suitable  freshets  in  the  streams.  During 
1947  virtually  the  same  situation  existed.  A  few  hitch  ran  during  the 
middle  of  March  after  a  light  rain.  That  only  a  small  segment  of  the  popu- 
lation spawned  during  this  run  is  indicated  by  the  "ripeness"  of  19  adult 
females  captured  in  Clear  Lake  on  March  19th  and  20th.  On  April  17th 
pumping  operations  were  initiated  on  Tule  Lake,  a  reclamation  on  Seotts 
Creek  about  three  miles  above  the  point  at  which  the  observations  were 
made.  As  a  result,  30,000  gallons  per  minute  were  discharged  into  a  stream 
previously  flowing  about  5,000  gallons  per  minute.  This  created  an  arti- 
ficial freshet.  Pumping  operations  started  at  noon  and  by  4  p.m.  spawning 
fish  were  present  on  the  riffle  under  study,  whereas  none  had  been  there 
during  the  morning.  Examination  of  several  other  tributaries  of  Clear 
Lake  the  next  day  revealed  no  hitch.  It  is  believed  that  a  rain  sufficient  to 
freshet  the  streams  at  this  time  would  have  caused  a  general  hitch  run  in 
all  streams.  Further  indication  that  all  hitch  did  not  spawn  in  1947  is 
given  by  the  gill  net  capture  on  June  24,  1947,  of  two  female  hitch  with 
freely  running  eggs. 

Vagaries  in  spring  rains  are  the  greatest  single  hazard  to  successful 
hitch  spawning.  If  the  rains  are  sufficient  to  cause  the  fish  to  spawn,  the 
majority  of  the  eggs  may  perish  before  hatching  through  a  sudden  drop 
in  the  flow,  exposing  the  gravels  before  the  fry  become  free-swimming. 
This  danger  is  accentuated  by  the  comparatively  long  development  period 
and  by  the  fact  that  spawning  coincides  with  the  end  of  the  rainy  season. 
In  past  years  there  have  been  times  when  the  streams  have  dropped  so 
rapidly  that  the  spawning  fish  were  stranded.  Kelsey  Creek,  tributary  to 
Clear  Lake,  has  been  so  choked  with  stranded  fish  that  one  could  literally 
walk  across  the  stream  on  the  backs  of  fish. 


106  CALIFORNIA   FISH   AND    GAME 

A  more  subtle  factor  in  the  decline  of  the  hitch  is  the  erosion  which 
the  drainage  has  suffered  at  the  hand  of  man.  As  it  affects  the  hitch,  this 
abuse  is  focused  on  the  graveling-in  of  stream  channels,  causing  surface 
flows  to  disappear  prematurely,  and  the  destruction  of  protective  cover 
by  overgrazing  and  fires  causing  the  rainfall  to  runoff  more  rapidly.  These 
two  factors  are  interdependent. 

It  is  apparent  that  a  series  of  years  in  which  weather  conditions  are 
unfavorable  can  cause  a  marked  reduction  in  the  hitch  population  and 
equally  apparent  that  a  series  of  good  years  can  build  up  the  population 
enormously,  in  view  of  the  large  number  of  eggs  produced  by  the  indi- 
vidual female. 

Post  Larval  Life 

On  May  16,  1947,  the  average  size  of  the  hitch  fry  in  Scotts  Creek 
was  2.2  centimeters.  On  May  28th  it  was  2.5  centimeters  (one  inch).  By 
the  end  of  the  first  week  in  June  young  hitch  were  virtually  gone  from 
Scotts  Creek  and  coincident  with  this  they  appeared  in  the  upper  end  of 
Clear  Lake  in  fairly  large  numbers,  so  it  can  be  inferred  that  they  migrate 
downstream  shortly  after  reaching  a  length  of  2.5  centimeters  or  at  an 
age  of  about  one  month.  A  sample  seined  in  Clear  Lake  on  June  9th  con- 
sisted of  fish  3.3  centimeters  in  average  length.  By  June  17th  they  had 
grown  to  4.1  centimeters  in  length.  By  July  10th,  the  average  size  was 
4.4  centimeters. 

By  August  1st  none  were  taken  in  a  series  of  20  seine  hauls.  The  best 
explanation  is  that  the  young  hitch  when  they  first  enter  the  lake  live  in 
the  littoral  zone  associated  with  young  bluegill  sunfish  (Lepomis  macro- 
cJiirus),  feeding  on  small  insects  and  plankton.  After  reaching  a  size  of 
approximately  5  centimeters  (2  inches)  they  range  the  entire  lake,  feed- 
ing on  plankton.  An  alternate  explanation  is  that  the  numbers  of  young 
fish  were  so  reduced  by  predation  that  they  were  present  during  August 
in  too  small  numbers  to  be  detected.  This  does  not  seem  probable  to  the 
writer,  in  view  of  the  comparative  ease  with  which  they  were  seined  dur- 
ing June  and  July.  Very  probably  the  individual  fish  as  they  reach  a 
certain  size  become  open-water  inhabitants,  gradually  reducing  the 
density  of  the  littoral  population. 

The  open-water  habits  of  the  hitch  make  it  an  ideal  forage  fish  for 
a  large  lake  since  in  ranging  the  lake  they  provide  forage  in  the  open 
waters,  in  contrast  with  bluegills,  which  afford  forage  in  the  littoral  zone 
only. 

Growth  Rate 

Figure  34  illustrates  the  growth  rate  of  the  hitch  as  calculated  from 
scales,  a  typical  example  of  which  is  illustrated  by  Figure  35.  It  can  be 
seen  that  males  of  comparable  age  are  smaller  than  females  and  that  they 
remain  in  the  forage  fish  class  into  their  second  year.  Most  of  the  fish  on 
which  Figure  34  is  based  were  taken  from  the  spawning  run;  so  the 
individuals  are  at  the  end  of  the  year  of  life  indicated  since  the  annulus 
can  be  expected  to  form  in  the  immediate  post-spawning  period.  The 
length-weight  relationship  is  illustrated  by  Figure  36. 


SACRAMENTO    HITCH 


107 


Length- Inches 
5 6         7 


10 

T- 


11 


(0  15  20 

Length-Centimeters 

Figure   34      The  Growth  Rate  of  Hitch  in  Clear  Lake,  1946-1947 


108 


CALIFORNIA   FISH   AND   GAME 


Figure  35.  Scale  from  a  Female  Hitch  24.2  Centimeters 
in  Length  Taken  April  19,  1947,  in  Scotts  Creek.  The  fish  is 
in  Age  Class  2. 


500 
^50 


^0 


g3» 


300 


S.20O 


150 


too 


So 


Length  -Inches 
^         -3       ,4^        5         4         7         g         9         10        11        a        (3 


10  15  10  25 

Length -Cenhwete  rs 


30 


19 
IT 

IS 


;3 

<o 

(LI 

11 

O 
K 

II 

:i 

O 

10 

1 

•+-. 

7 

j; 

o. 

a 

^ 

7^ 


i 

5 

■3 

2 

■/ 


Figure   36.      The  Length-weight  Relation   of  Hitch,   Clear  Lake,   1946-1947. 

Curve  fitted  by  eye 


SACRAMENTO    HITCH  109 

Discussion 

The  nonadhesive  eggs  of  the  hitch  with  their  protective  cushion  are 
unusual  in  cyprinid  fishes.  They  generally  have  adhesive  eggs  and  no 
noticeable  cushion.  In  an  adhesive  egg  a  cushion  is  unnecessary  since  the 
eggs  are  securely  fastened  in  a  safe  place.  The  hitch  eggs  are  adapted  to 
their  haphazard  deposition  in  gravels  which  are  subject  to  considerable 
shifting.  It  is  hard  to  imagine  a  high  survival  of  these  eggs  without  this 
cushion. 

Miller  (1945)  reported  numerous  hybrids  (Lavinia  exilicaiida 
harengus  x  Hesperoleucus  symmetricus  suiditus)  in  the  Pajaro  River 
system.  Normally  Hesperoleucus,  a  much  smaller  cyprinid  inhabiting 
streams  only,  spawns  in  shallow  water  with  very  slight  current.  Its  eggs 
are  adhesive  and  are  deposited  under  rocks.  In  addition,  spawning  takes 
place  when  the  streams  are  clear  and  have  subsided  from  the  spring 
freshets.  However,  if  the  stream  flow  regime  was  such  that  adult  hitch 
were  trapped  in  pools  inhabited  by  Hesperoleucus  they  might  extrude 
eggs  and  sperm  in  areas  in  which  Hesperoleucus  were  spawning. 

In  Clear  Lake  hitch  apparently  have  been  unable  to  spawn  success- 
fully since  1943  or  1944.  This  means  that  the  supply  of  forage  fish  has 
been  considerably  lowered  and  it  is  believed  that  this  is  one  of  the  chief 
factors  causing  a  decline  in  the  Clear  Lake  sport  fishery.  There  are  in 
addition  other  forage  fishes  which  have  been  greatly  reduced  in  Clear 
Lake  in  recent  years. 

Summary 

The  hitch,  Lavinia  exilicauda  (family  Cyprinidae),  is  a  valuable 
forage  fish.  Juveniles  feed  on  plankton  and  small  insects,  and  adults 
almost  exclusively  on  plankton. 

The  hitch  is  a  stream  spawner,  running  into  the  streams  in  late 
spring.  The  females  first  spawn  at  the  end  of  their  first  year ;  and  females 
at  the  end  of  their  third  year  (age  class  2) .  Spawning  takes  place  in  riffle 
areas.  The  eggs  sink  and  lodge  in  crevices  in  the  gravel,  but  are  non- 
adhesive.  Shortly  after  deposition  the  egg  absorbs  water,  and  the  space 
between  the  membrane  and  the  yolk  fills  with  liquid,  protecting  the 
developing  embryo.  Development  up  to  the  free-swimming  stage  prob- 
ably takes  about  20  days  at  62  degrees  F.  Success  of  reproduction  is  com- 
pletely dependent  on  run-off.  This  fact,  coupled  with  the  fecundity  of 
the  hitch,  results  in  marked  fluctuations  in  the  population. 

The  young  migrate  to  the  lake  shortly  after  reaching  a  length  of  2.5 
centimeters  (1  inch).  The  juveniles  occupy  the  littoral  zone  of  the  lake 
until  they  are  approximately  five  centimeters  (2  inches)  in  length,  after 
which  it  is  believed  that  they  become  open-water  inhabitants.  As  an  open- 
water  forage  fish  they  fill  a  need  in  a  large  lake,  whose  productivity,  if 
dependent  on  bluegill,  sunfish,  would  be  limited  to  the  littoral  zone.  Males 
of  comparable  age  are  smaller  than  females. 


110  CALIFORNIA   FISH    AND    GAME 

References 

Lindquist,  A.  W.,  C.  C.  Deouier,  and  J.  E.  Hancey 

1943.     The  Relationship  of  Fish  to  the  Clear  Lake  Gnat  in  Clear  Lake,  California. 
Calif.  Fish  and  Game,  vol.  29,  no.  4,  pp.  196-202. 
Miller,  R.  R. 

1945.  The  status  of  Lavinia  ardesiaca,  a  Cyprinid  Fish  From  the  Pajaro-Salinas 
River  Basin,  California.  Copeia  1945,  no.  4,  pp.  197-204. 

Rutter,  C. 

1908.  The  Fishes  of  the  Sacramento-San  Joaquin  Basin,  With  a  Study  of  Their 
Distribution  and  Variation.  Bull.  U.  S.  Bur.  Fish.  vol.  XXVII,  1907,  pp. 
103-152,  pi.  V. 

Shapovalov,  Leo 

1940.     Unpublished  Notes  on  Spawning  Hitch  in  Lake  County.  April  13,  1940. 

Snyder,  J.  O. 

1913.  The  Fishes  of  the  Streams  Tributary  to  Monterey  Bay,  California.  Bull. 
U.  S.  Bur.  Fish.,  vol.  XXXII,  1912,  pp.  47-72,  pis.  XIX-XXIV. 


KOKANEE  IN  CALIFORNIA 

By  Bria:x  Curtis  and  J.  C.  Fraser  ^ 

Bureau  of  Fish  Conservation 
California  Division  of  Fish  and  Game 

The  "kokanee"  {Oncorhynchus  nerha  kennerlyi)  was  first  planted 
in  California  waters  in  1941.  This  is  a  landlocked  form  of  the  Pacific 
sockeye  or  red  salmon.  It  is  native  to  the  Pacific  Northwest,  where  it  is 
also  called  "little  redfish"  and  "silver  trout."  Under  highly  favorable 
conditions  it  may  reach  a  size  of  five  pounds.  Twelve  to  fourteen  inches  is 
average,  and  under  poor  conditions  it  never  exceeds  eight  inches. 

It  is  preeminently  a  lake  resident,  and  may  spawn  on  gravelly  lake 
shores  as  well  as  in  streams  connecting  with  lakes.  It  matures  and  spaT\Tis 
at  the  end  of  its  third  or  its  fourth  year,  and  like  all  Pacific  salmons  dies 
after  spawning.  It  prefers  cool  waters,  and  therefore  goes  deeper  as 
temperatures  rise  in  summer.  Although  its  food  is  made  up  largely  of 
plankton,  the  minute  animals  which  drift  in  the  water,  it  can  be  easily 
taken  in  some  lakes  on  hook  and  line  in  spring  and  autumn.  In  summer 
it  is  harder  to  catch.  Trolling  with  flashers  and  baited  hook,  and  still- 
fishing  a  few  feet  off  bottom,  are  favored  methods ;  fly-fishing  can  be 
successful  in  the  late  afternoon  in  spring  or  fall  when  the  fish  are  near 
the  surface.  The  kokanee  puts  up  a  good  fight,  but  has  a  tender  mouth 
and  is  hard  to  land.  It  is  excellent  eating.  In  its  native  regions  it  has 
furnished  abundant  fishing  and  is  looked  upon  as  a  valuable  element  in 
the  angling  resources. 

The  decision  to  introduce  it  to  California  was  based  in  part  on  its 
popularity  in  certain  sections  of  the  northwest,  and  in  part  on  its  plank- 
ton feeding  habits,  which  suggested  that  it  might  do  well  in  reservoirs 
where  fluctuations  made  for  poor  production  of  bottom  food.  Salt  Springs 
Reservoir  on  the  North  Fork  of  the  Mokelumne  River  off  the  Carson  Pass 
Road  was  selected  for  the  initial  test ;  its  level  fluctuates  extensively,  and 
it  is  so  located  that  little  harm  could  be  done  if  the  kokanee  turned  out 
to  be  an  undesirable  citizen.  One  hundred  thousand  eggs  obtained  in  late 
1940  from  Idaho  through  the  U.  S.  Fish  and  Wildlife  Service  were 
hatched  at  the  Basin  Creek  State  Fish  Hatchery  near  Sonora,  and  67,000 
fingerlings  were  planted  in  July  of  1941  at  a  length  of  a  little  under 
two  inches.  (In  the  State  of  Washington,  incidentally,  where  great  num- 
bers of  this  species  are  produced,  planting  at  a  very  small  size  is  favored.) 
The  Salt  Springs  area  was  closed  shortly  thereafter  as  a  war  measure, 
but  tests  in  the  spring  of  1943  showed  the  kokanee  to  be  abundant  and 
easily  caught,  at  a  size  of  about  10  inches.  In  November  of  1943,  at  the 
end  of  their  third  year,  and  at  a  length  of  11  to  12  inches,  they  were  ready 
to  spawn,  and  some  300,000  eggs  were  taken  from  626  females.  A  total  of 
over  3,000  fish  were  caught  in  seines  at  this  time,  4^  percent  of  the  num- 
ber planted,  and  since  many  more  were  present  than  were  netted,  a  good 
survival  was  indicated. 


1  Submitted  for  publication  March,  1948. 


(Ill) 


112 


CALIFORNIA   FISH   AND    GAME 


Figure  37.     Kokanee  from   Salt   Springs  Reservoir,   November,    1943.   Female  in 
center,  male  below  and  above.  Photograph  by  Malcolm  Wilson 

These   results  were  sufficiently  encouraging   to   warrant  further 
stocking,  which  has  been  carried  out  as  shown  in  the  following  table : 

STOCKING   OF    KOKANEE    IN    CALIFORNIA 

Size  in 
Name  of  Date  of  Source  Number       numbers 

water  planting  of  eggs  planted  per  oz. 

Salt  Springs  Reservoir, 

Amador  County 1941—7/12-16  Idaho  67,000  27 

Strawberry  Lake  (also  called 
Pinecrest),  Tuolumne 

County 1944—8/12-10.       Salt  Springs       106,000  22-32 

1945—7/28  Montana  99,000        -  25-40 

8/6 
1947—5/28  Washington        284,000         140-265 

6/16 
Waterhouse  Lake,  Tuolumne 

County 1944—8/3  Snlt  Springs  700  32 

Echo  Lake,  El  Dorado 

County 1944—7/5-20  Montana  69,000  51-72 

1945—8/2-7  Montana  79,000  52 

Donner  Lake,  Nevada 

County  ___, 1944—6/22  Montana  83,000        270-280 

7/19 
1945—8/8-8  Montana  74,000  52 

1947—5/28  Washington       100,000  265 

NOTE: 

Average  lengths  of  flsh  are  approximately: 
13  Inches  at    25  per  ounce. 
li  Inches  at  '50  per  ounce. 
I   inch    at  100  per  ounce. 


KOKANEE  113 

The  results  have  been  uneven.  Echo  Lake  has  been  the  most  dis- 
appointing. In  this  high,  rocky  basin  it  has  been  very  difficult  to  produce 
good  fishing,  and  it  was  hoped  that  the  plankton-eating  kokanee  would 
solve  the  problem.  However,  growth  has  been  poor  here,  the  fish  not 
exceeding  eight  to  nine  inches  at  maturity,  and  anglers  have  shown  little 
interest  in  them.  Strawberry  Lake  has  provided  the  best  fishing,  espe- 
cially when  it  was  drawn  down  in  late  summer  of  1946 ;  large  catches 
were  made  at  this  time,  with  the  kokanee  reaching  a  size  of  10  inches. 
Donner  Lake  has  produced  the  largest  fish,  the  spawners  running  from 
12  to  16  inches.  The  kokanee  aroused  little  angler  interest  here  at  first, 
but  their  popularity  seems  to  be  growing,  and  more  are  being  caught 
every  season." 

Kokanee  have  appeared  in  other  waters  than  those  in  which  they 
were  planted.  About  100  were  found  in  December,  1946,  spawning  in  the 
small  stream  formed  by  the  water  running  from  the  Tahoe  Hatchery  into 
the  lake.  These  had  evidently  escaped  in  1944  from  the  hatchery  troughs 
where  they  were  reared,  and  were  returning  to  the  "home  stream." 
In  the  Truckee  River  spawning  kokanee  appeared  just  below  the  Tahoe 
Dam  in  the  winter  of  1947-1948 ;  these  are  presumed  to  have  migrated 
out  of  Donner  Lake.  And  in  1946  a  number  of  Kokanee  went  out  of  Straw- 
berry with  the  declining  water  and  down  to  Lyons  Reservoir.  In  no  case 
has  any  harm  come  from  the  escape  of  kokanee  into  other  waters,  nor  is 
any  possibility  of  harm  foreseen. 

In  California  all  kokanee  so  far  observed  have  matured  at  the  end 
of  their  third  year.  Kokanee  were  seen  spawning  by  the  junior  author 
in  Donner  Lake  in  November  of  1947,  in  water  varying  in  depth  from 
one-half  to  three  feet,  and  from  right  along  the  shore-line  to  20  feet  out. 
Concentrations  of  fish  were  found  near  the  mouths  of  the  small  inlet 
streams  on  the  north  side  where  the  lake  bottom  was  sandy  with  some 
pebbles  and  a  few  rocks,  and  many  also  spawned  along  the  north  shore 
where,  water  trickled  in  from  the  road  culverts.  Water  temperature  was 
45  degrees  Fahrenheit. 

The  spawning  pattern  insofar  as  it  could  be  observed  resembled  that 
described  by  Schultz  (1937),  with  such  differences  in  detail  as  might  be 
attributable  to  stream  spawning  in  Schultz 's  report  as  against  lake 
spawning  here.  Only  one  female  was  seen  in  the  process  of  building  a 
nest,  and  unfortunately  she  was  in  the  center  of  a  group  of  fish  where 
it  was  impossible  to  follow  her  actions  closely,  or  those  of  any  males 
involved.  She  apparently  rolled  over  on  her  side  and  dug  vigorously  with 
the  posterior  part  of  her  body  for  a  few  seconds,  then  circled  away  from 
the  nest;  occasional  interruptions  would  be  caused  by  a  general  milling 
around  of  all  the  fish  in  the  vicinity.  Actual  pairing  of  fish  seemed  to  be 
the  rule. 

Spawning  activity  began  by  male  and  female  circling  the  nest,  one 
behind  the  other.  Eventually  the  female  would  pass  over  the  center  of 
the  nest,  and  come  to  a  stop  there — sometimes  on  the  first  pass,  and  some- 
times on  the  second  or  third.  The  male  would  then  join  her,  and  both 
would  vibrate  at  which  time  it  is  presumed  that  the  sex  products  were 
deposited.  The  female  invariably  dug  into  the  sand  near  the  end  of  the 
vibrations,  raising  a  small  cloud  of  fine  particles.  All  of  this  took  about 


2  Reports  from  Donner  Lake  received  after  this  paper  went  to  press  tell  of  excel- 
lent fishing  in  May,  1948,  with  many  limit  catches  of  kokanee  weighing  about  one 
pound  each. 


114  CALIFORNIA   FISH    AND    GAME 

10  seconds,  after  which  circling  was  resumed.  Individual  pairs  were  seen 
to  repeat  this  process  four  or  five  times  over  the  same  nest,  presumably 
with  deposition  of  eggs  each  time.  Covering  of  the  eggs  was  apparently 
accomplished  by  the  digging  action  of  the  female  at  the  end  of  each 
period  of  vibrations,  but  it  is  possible  that  a  further  and  final  covering 
took  place  after  the  completion  of  egg  deposition  in  any  particular  nest. 
Unfortunately  Donuer  Lake  was  drawn  down  very  heavily  in  Janu- 
ary and  February,  and  all  of  these  spawning  beds  were  left  high  and 
dry  in  frozen  ground. 

Reference 

Schultz,  Leonard  P. 

1937.     The  Breeding  Habits  of  Salmon  and  Trout.     Report  of  the   Smithsonian 
Institution  for  1937,  pp.  365-376. 


EXPERIMENTS  ON  THE  MANAGEMENT  OF 
COLORADO  RIVER  BEAVER' 

By  Arthur  L.  Hensley  ^  and  B.  C.  Fox  ^ 

Introduction 

The  Colorado  River  or  Sonora  Beaver  (Castor  canadensis  repen- 
tinus  Goldman)  in  that  portion  of  the  Colorado  River  constituting  a 
common  boundary  between  the  States  of  California  and  Arizona  presents 
a  joint  management  problem  requiring  mutual  understanding  and  uni- 
formity in  the  adoption  of  regulations  or  policies  by  the  state  game 
departments. 

The  development  of  a  beaver  resource  management  plan  is  influenced 
by  two  major  considerations :  that  which  is  to  the  best  interest  of  this 
resource  of  the  two  states,  and  that  which  is  most  feasible  from  the 
standpoint  of  administration  by  the  two  game  departments  charged 
with  this  responsibility.  Further  work  is  in  progress,  and  the  express 
purpose  of  this  paper  is  to  record  the  preliminary  findings  of  the 
cooperative  program  as  undertaken  by  the  two  game  departments. 

The  authors  wish  to  express  their  sincere  appreciation  to  those 
members  of  the  California  Division  of  Fish  and  Game,  Arizona  Game 
and  Fish  Commission,  United  States  Fish  and  Wildlife  Service,  and 
others  who  participated  in  the  annual  surveys  and  other  functions  of 
the  program.  Thanks  are  also  due  to  the  trappers  employed  in  the  pro- 
gram for  their  timely  suggestions  and  cooperation. 

This  program  presented  the  two  states  with  an  opportunity  to  collect 
data  relative  to  methods  of  procedure  applicable  to  future  management 
plans  for  other  parts  of  either  state.  It  was  therefore  agreed  to  use  the 
Colorado  River  as  a  proving  gr-ound  upon  which  to  experiment  and,  if 
possible,  demonstrate  the  potential  value  of  the  beaver  resource  under 
a  plan  of  share  cropping  by  managed  trapping. 

Since  the  regulations  governing  operations  of  the  Arizona  Game 
Department  permit  more  freedom  of  operation  than  those  of  the  Cali- 
fornia agency,  it  was  agreed  that  Arizona  would  assume  supervision  and 
administration  of  the  program  on  the  basis  of  joint  acceptance  of  recom- 
mendations resulting  from  cooperative  surveys  made  by  representatives 
of  both  states. 

Objectives 

To  secure  and  record  as  much  information  as  time  permitted  relative 
to  such  important  points  as : 

1.  Development  of  a  practical  technique  for  estimating  numbers  of 
beaver  that  can  be  safely  harvested  from  a  given  area  or  portion 
of  a  stream  on  the  basis  of  a  sustained  annual  yield. 

1  Submitted  for  publication  April,  1948.  A  portion  of  this  study  wa.s  part  of  Fed- 
eral Aid  in  Wildlife  Restoration  Project  California  5-R  ;  a  survey  of  the  fur  resources 
of  the  State  of  California. 

=  Bureau  of  Game  Conservation,  California  Division  of  Fish  and  Game. 

'  Arizona  Game  and  Fish  Commission. 

(  115  ) 


116 


CALIFORNIA   FISH   AND    GAME 


2.  Determination  of  the  most  feasible  and  economical  plan  of  har- 
vesting beaver  with  employed  trappers, 

3.  Types  and  use  of  equipment  necessary  for  the  successful  opera- 
tion of  such  a  plan. 

4.  Methods  of  marketing  to  obtain  the  greatest  monetary  returns. 

5.  Determination  of  occurrence  of  disease  in  Colorado  Kiver  beaver. 

6.  Collection  of  weights  and  measurements  of  adult  beaver. 


J<'niiii(i';   :;n.     iVlirst  of   iliii  .survey  was  performed  in  small   boats  powered 

by  outboard  motors 

Methods 

The  first  joint  survey  of  the  Colorado  River  beaver  was  undertaken 
in  September  of  1943  and  thereafter  in  October  for  the  four  subsequent 
years. 

The  initial  procedure  involved  crisscrossing  the  river  from  bank  to 
bank  wherever  the  channel  permitted,  making  counts  of  beaver  lodges  or 
houses,  freshly  used  beaver  slides,  beaver  bank  burrows,  beaver  scent 
mounds,  and  general  observations. 

The  recording  of  beaver  bank  burrows  excavated  in  the  stream  banks 
was  attempted  during  the  first  three  surveys  and  thereafter  discontinued. 
It  was  found  that  these  counts  could  not  be  made  with  anj^  degree  of 
accuracy  because  of  almost  daily  water  level  fluctuations  due  to  controls 
exercised  at  Boulder  Dam  located  approximately  60  miles  above  the  upper 
boundarj^  of  the  study.  These  counts,  consequentlj^  were  of  no  value  for 
comparative  analysis  in  attempting  to  measure  beaver  population  density 
in  the  river.  Due  to  frequent  blockage  by  sand  bars  during  low  water 
periods  of  the  day,  it  was  difficult  to  obtain  counts  of  the  beaver  slides  at 
such  sites.  It  is  estimated  that  Table  1  represents  about  40  percent  of  the 
total  number  of  the  beaver  slides  and  80  percent  of  the  beaver  houses 
present  in  the  river  for,  theoretically,  only  50  percent  of  the  beaver  slides 
would  have  been  observed  and  counted  by  the  method  used.  No  beaver 
dams  were  observed  in  the  Colorado  River. 


MANAGEMENT    OF    BEAVER 


117 


Figure  39.     Newly  constructed  beaver  lodge  on  bank  of 
Colorado  River  above  Needles,  California 


Figure  40.     A  beaver  lodge  constructed   in  midstream 
below  Blythe,  California 


118 


CALIFORNIA   FISH   AND    GAME 


Figure  41.     A    typical    beaver   slide   or   runway   showing 

recent  use 


MANAGEMENT    OF   BEAVER 


119 


VI 


Figure  43.     Shore  cover  on  Colorado  River  between  Imperial  and  Laguna  Dams. 
This  characteristic  stand  contains  an  abundance  of  willow 


General  observations  for  the  most  part  were  limited  to  the  abundance 
of  principal  food  plants  and  degree  of  utilization  in  reference  to  the 
potential  carrying  capacity  in  given  portions  of  the  stream.  Food  plants 
consist  largely  of  cattail  {Typha  latifolia),  tule  {Scirpus  acutiis),  willow 
(Salix  spp.),  Cottonwood  (Populus  fremontii),  salt  sedar  {Tamdrix 
galica),  arrowweed  (Pluchea  sericea)  and  water  wally  {BaccJinris  gluti- 
nosa).  Although  extensive  cutting  of  cottonwoods  and  willows  were 
observed  in  several  locations,  there  were  only  a  few  spots  where  over- 
utilization  of  food  plants  had  become  critical. 

A  number  of  residents  living  adjacent  to  the  river  were  interviewed 
to  obtain  information  relative  to  poaching  and  display  of  interest  in  the 
attempted  management  of  this  resource  by  the  states. 

No  effort  was  made  to  ascertain  actual  numbers  of  beaver  present  in 
the  river  as  this  would  have  required  more  time  than  was  available. 
Rather  emphasis  was  placed  on  two  major  objectives  :  (1)  the  determina- 
tion of  the  comparative  density  of  the  population  in  various  sections  of 
the  river  and  (2)  the  development  of  a  yardstick  to  estimate,  with  rea- 
sonable accuracy,  the  number  which  can  safely  be  removed  without 
adverse  influence  on  the  distribution  of  the  population,  assuring  a  suffi- 
cient residue  of  seed  stock  to  produce  a  harvestable  yield  year  after  year. 


120 


CALIFORNIA   FISH   AND   GAME 


The  river  was  arbitrarily  divided  into  sections  for  the  purpose  of 
recording  data  to  use  later  as  a  basis  for  future  operations,  numbered 
as  follows : 

1.  Intersection  of  the  California,  Arizona,  and  Nevada  boundaries 
to  Needles,  California. 

2.  Needles,  California,  to  Topock,  Arizona. 

3.  Topock,  Arizona,  to  Parker  Dam. 

4.  Parker  Dam  to  Headgate  or  Squaw  Dam. 

5.  Headgate  or  Squaw  Dam  to  Blythe,  California. 

6.  Blythe,  California,  to  Imperial  Dam. 

7.  Imperial  Dam  to  California-Mexico  boundary. 

Certain  of  these  river  sections  were  grouped  together  and  designated 
as  trapping  units  as  follows : 

1.  Intersection  of  California,  Arizona,  and  Nevada  boundary  to 
Topock,  Arizona  (Comprising  river  sections  1  and  2). 

2.  Parker  Dam  to  Blythe,  California  (Comprising  river  sections  4 
and  5). 

3.  Blythe,  California,  to  California-Mexico  boundary  (Comprising 
river  sections  6  and  7). 


Figure  44.     Beaver  cuttings  between  Squaw  and  Parker 
Dams  demonstrating  overutilization 


MANAGEMENT    OF   BEAVER 


]21 


\  NE  VADA 


THE    JOINT 
ARIZONA- CALIFORNIA 
COLORADO    RIVER 
BEAVER    PROJECT 


SCALE  or 

MILES 

0    l.a  IC         If       JO 


<^,, 


MEXICO 


Figure  45.     Map  indicating  the  river  sections  used  as  subdivisions  in  this  study 


122  CALIFORNIA    PISH    AND    GAME 

River  section  3,  comprising  all  of  Lake  Havasu  (formed  by  Parker 
Dam),  is  not  included  as  the  habitat  was  destroyed  by  the  creation  of  the 
lake  and  will  require  several  years  to  redevelop  sufficient  food  supply  to 
support  more  than  a  limited  number  of  beaver. 

The  census  methods  employed  to  obtain  data  were  relatively  the 
same  each  season  except  that  the  1947  survey  counting  was  done  by  one 
individual  whereas  in  previous  surveys  two  or  more  participated  in  mak- 
ing counts.  The  1947  method  resulted  in  a  lesser  area  of  each  bank 
counted ;  consequently  the  total  count  in  comparison  to  the  former  sur- 
veys was  lowered.  This  does  not  necessarily  indicate  a  lowering  in  the 
trend  of  population. 

The  data  presented  in  Table  1  is  only  useful  on  a  long  term  basis. 
In  its  present  form  it  is  indicative  rather  than  conclusive  except  for  the 
trend  of  density  in  population  which  has  more  or  less  remained  constant 
in  relation  to  the  numbers  of  beaver  removed. 

Not  including  those  beaver  poached  (of  which  some  evidence  was 
found)  it  was  recommended  that  1,150  beaver  be  harvested  of  which  1,054 
were  taken  during  the  course  of  the  four  seasons  included  in  this  analysis. 

Due  to  wartime  rationing  of  gasoline  and  tires,  shortages  of  mate- 
rials and  supplies,  limited  personnel,  and  inability  on  the  part  of  Cali- 
fornia to  lend  the  necessary  assistance  in  supervising  the  program,  the 
animals  were  not  taken  as  recommended.  The  quota  was  determined  after 
study  of  the  survey  data  by  discussion  among  the  personnel  involved 
based  on  their  past  experiences  and  what  they  thought  to  be  a  logical 
number  to  yield  results  possible  of  analysis  and  still  be  within  the  limits 
of  surplus  animals. 

It  is  evident  that  the  evolution  of  any  systematic  management  plan 
from  Table  1  is  at  present  questionable  since  the  recommendations  were 
not  followed  during  the  1943  and  1944  seasons.  The  take  was  either  too 
few  or  too  many,  but  it  is  hoped  that  in  the  future  conditions  will  permit 
the  carrying  out  of  the  program  as  planned  and  in  accordance  with  annual 
recommendations. 


MANAGEMENT    OF    BEAVER 


123 


lij 

CQ 
< 


(8 

Q 
> 

3 

(0 


1 
J 

J 

5 
Z 

05 

OOO  O  OO      'o 

; 

o                 I 

to               S^ 

CQ* 

ooooo»cc;(M      CO               >vO 
CO      ■^t--«j«      cfl               6^ 

-    w    «          c<I                     ^ 

QO 

•* 
2 

t--o  o  coo  r-     'oc 

^                 t^Tj*  Oi       •!>- 
CQ  C^       • 

2           ^5 

CO 

2 

»r30  OO  cc  o     !  r^ 

-3 

E 

c 
o 

s 

«5 

OS 

oooooo    lo 

o                1 

• 

CO 

oooooo    'o 

o 

1 

OS 

oooooo    '  o 

150 

6.7% 

i 

lOO  O  »f5  o  o      ■  o 

CO         •—  t^  to  O      1  O 

to                  ir^ 

CO 

■^ 

1— t 

tCOOuDOO'O        O                     >.o 
t—             t^OiO      'O        O                   o^ 

—  '->—*         »0                     IM 
'          1                          c^ 

03 

8. 

2 

OOCC  !MCO  —  —       Icq 
<MCO       ' 

OO                            1 

i 

CO 

05 

i>-coiccoco  O     ■  -^ 

"  CI  CC       ' 

: 
CO           ; 

en 

!>■  Tt< -^  CO  I~^  O       '  OO 

; 

CO                            1 

OS 

^  :  :2gg  i^ 

§          i 

CO 

2 

1      ^  ^^    ,    , 

■^                  1 

CO                            f 

t-l 

r3 

OS 

T-H 

O  OOO— <  OCD      1  CO 

OO                         I 
CO                         ' 

CO 
OS 

CO  «0  lO  CO  t^  iC       'CO 

CO  O;  CQ  —  Oi»0       'CO 
(M  to  oc       '  -< 

CO                   ! 

o          : 

CQ                            I 

05 

^^COCOO:  U5CO      ■  OO 
^  -*         CO  -^  O       'CO 
f-H                CO  CO  t^       ■  CO 

CQ                            I 

ci"            ; 

CO      "      1  --  CicO      '  — • 

en     1     <  CO— "M     '  OO 
Oi      '      1  '^J'  ^^      '  ■* 

o                   • 

CO                            ' 

oq                   1 

CO 
OS 

^  lO      t-^Cfl  C«       i  o 

r- t-»     1  CO  c^  *o     1  Tt< 

■^                  1 

App. 
river 
miles 

O^CQ  ^iC-**«       lo 
•-"•-' CO  ^  to  lO       'CQ 

CO                            " 

OS                         ' 

s 

.2 

^  CQ  CO  -^  toco         1* 

Totals 

Percentages  based 
on  total  beaver 
slides 

O 


a.t: 


bfl 

c  .. 

i:z 

•a 

«  " 

75  ^ 

en 

C    CD 

«•= 

C:  5 

SI'' 

So 

g  _o 

•u^ 

2  i' 

o^- 

Sf 

s:  S 

c 

a> 

*)^ 

^i 

s^ 

C  — 

<u  ?^ 

CJ   C 

^  rt 
M  w 

«i 

—  i-  s  ^ 
n  ■-  i;  S 


02" 

■^00  COi-H 


124 


CALIFORNIA    FISH   AND    GAME 


Management  Procedure 

Methods  were  modified  during  each  season's  procedure  in  an  effort 
to  determine  the  plan  best  suited  to  the  successful  operation  and  manage- 
ment of  the  activities.  The  two  procedures  given  trials  to  date  were 
roughly  as  follows : 


Procedure  1 

1.  Employment  of  salaried  trappers 
including  a  $1  bonus  per  pelt  for  well- 
handled  pelts  rather  than  a  share  basis. 
All  equipment  such  as  boat,  motor,  traps, 
and  personal  belongings  furnished  by  the 
trapper ;  incidental  supplies  and  repairs 
were  furnished  by  the  State  Game  depart- 
ments. 

2.  The  number  of  trappers  required  to 
take  the  estimated  quota  were  employed 
and  supervised  by  the  State  of  Arizona. 

3.  The  cost  of  operations,  including 
salaries,  maintenance,  trapping,  pelting, 
transporting,  marketing,  etc.,  were  de- 
ducted from  the  total  revenue  from  the 
sale  of  pelts  and  the  balance  was  divided 
equally  between  California  and  Arizona. 

4.  All  other  fur  bearers  accidentally 
caught  by  trappers  during  trapping 
operations  were  to  be  saved,  prepared 
for  marketing,  included  in  the  sale  of 
pelts,  and  proceeds  were  to  be  equally 
divided  by  the  two  states.  Beaver  were 
trapped  from  the  river  proper.  The  river 
proper  was  defined  as  the  main  channel, 
all  true  sloughs  whose  channels  leave  and 
rejoin  the  main  river  whether  flowing 
through  during  the  period  or  not,  and  all 
tributaries  and  diversion  canals  for  a 
distance  of  one-half  mile  from  the  main 
channel. 

5.  The  State  of  Arizona  was  respon- 
sible for  the  sale  of  the  beaver  pelts  with 
the  proviso  that  the  pelts  be  sold  to  the 
highest  bidder  at  i)ublic  auction  and  that 
the  State  of  California  l)e  provided  with 
copies  of  the  l)ids  at  the  time  remittance 
was  made. 


Procedure  2 

1.  Trappers  were  paid  at  the  rate  of 
$5  per  pelt  and  were  provided  with  all 
equipment  with  the  exception  of  bedding, 
food,  and  other  personal  requirements. 
A  provision  was  included  to  permit  this 
rate  to  be  increased  to  $10  if  the  trapper's 
take  at  $5  per  pelt  did  not  provide  him 
with  an  adequate  wage. 

2.  The  necessary  number  of  trappers 
required  to  take  the  estimated  quota  were 
employed  and  supervised  by  the  State  of 
Arizona. 

3.  The  trapping  program  was  adminis- 
tered by  the  State  of  Arizona  and  all 
costs  of  operations  (including  equipment 
costs  incurred  by  both  states)  were  paid 
from  the  proceeds  of  the  sale  of  beaver 
pelts  and  50  percent  of  the  balance  was 
remitted  to  the  State  of  California. 

4.  Animals  were  trapped  only  from  the 
river  proper.  The  river  proper  was  defined 
as  the  main  channel,  and  all  true  sloughs 
whose  channels  leave  and  rejoin  the  main 
river  whether  flowing  through  during  the 
period  of  trapping  or  not,  and  all  tribu- 
taries and  diversion  canals  for  a  distance 
of  one-half  mile  from  the  main  channel. 

Trappers  while  engaged  on  this  project 
were  not  allowed  to  operate  trap  lines 
for  the  purpose  of  taking  fur  bearers 
other  than  beaver. 


.5.  The  sale  of  the  pelts  was  placed  in 
the  hands  of  one  of  the  Western  States 
Fur  Auction  Houses  for  marketing  at  the 
best  discretion  of  the  Fur  Auction 
Exchange  and  payment  for  pelts  was 
remitted  to  the  Arizona  Game  and  Fish 
Commission. 


During  the  1943  and  1944  seasons  trappinsr  activities  were  performed 
as  per  Procedure  1.  Allegedly  experienced  trappers  were  employed  from 
among  the  group  of  men  who  were  known  to  have  trapped  beaver  for 
many  years  along  the  Colorado  River. 

The  few  experienced  trappers  worked  a  very  short  time,  apparently 
prefpi-riiig  to  trap  elsewhere  rather  than  to  work  for  a  salary  of  $150  per 
month  plus  the  one  dollar  bonus  per  beaver,  with  the  result  that  it  became 
necessary  to  employ  inexperienced,  poorly  ccpiipped  trappers  to  continue 
the  operations  for  the  balance  of  the  season.  This  set  of  circumstances 


MANAGEMENT    OF   BEAVER 


125 


•?il^'iia^.:x^ 


L>. 


s-*Xt»    . 


Figure  46.     Riv^er  barge  set  up  on  trailer  for  transporta- 
tion from  one  trapping  headquarters  to  another 


B^^i^^.i.'-:.'^^'. 


Figure  47.  River  barge  assembled  for  use  by  trapping 
crew.  This  provided  living  quarters  as  well  as  working 
space. 

along  with  the  lack  of  adequate  equipment  and  knowledge  was  responsible 
for  the  virtual  failure  of  the  program  as  recommended  under  this  pro- 
cedure. 

Under  Procedure  2  three  crews  consisting  of  four  experienced  trap- 
pers and  their  helpers  followed  this  procedure  without  difficulty ;  in  fact, 
their  enthusiasm  was  so  great  that  710  beaver  (210  more  than  the  number 
recommended  for  harvesting)  were  removed  before  the  operation  was 
arbitrarily  halted. 


126 


CALIFORNIA   FISH    AND    GAME 


Costs 

The  following  items  of  equipment  were  purchased  by  the  two  game 
departments  to  insure  the  successful  prosecution  of  Procedure  2  : 

Numie)-  Items  Cost 

5     Outboard  motors,  1  22-h.p.  4  10-h.p $1,184  00 

1     Portable  store  room,  20'  x  24' 378  84 

3     Trapping  work  boats,  12'  x  4' 303  64 

3  River  scow  boats,  8'  x  20',  split  sections,  4'  x  20' 595  55 

4  Tents,  8'  x  12',  for  living  quarters  on  scow  boats 202  68 

4     Canfield  camp  stoves  with  ovens 26  00 

100     Traps,  size  14,  and  6  setting  clamps 270  85 

100     Drying  frames,  f"  bolt  stock  in  9'  lengths 32  98 

100     #12  gauge  smooth  wire 5  45 

Hand  tools  and  miscellaneous  supplies 363  52 


In  addition  there  were  other  incidental  items  of  equipment  and  sup- 
plies, such  as  gasoline  containers,  gasoline,  oil,  etc.,  purchased  during  the 
course  of  the  project. 

The  following  is  a  recapitulation  table  of  costs  incurred  for  opera- 
tions for  each  of  the  four  seasons  during  which  the  program  has  been  in 
effect : 

Trapping  Equipment  Miscel- 

Season                     contracts  purchases  Supplies  Repairs       laneous  Totals 

1943-44 $844  00  $88  68  $30  00  $962  68 

1944-45 3,6.57  00  $2,999  53  131  29  232  23     $1,606  83  8,790  50 

1945-46 1,100  00          328  51  152  54  289  06  1,870  36 

1946-47 350  00  16  25  61  10            437  35 

$5,951  00     $3,328  04     $398  76     $262  23     $1,956  99     $12,060  89 


,.^; 

*{^- 

A^i  •-?*• 

Figure  48.  Portable  storehouse  located  above  Fort 
Mohave,  Arizona,  u.sed  for  storage  of  equipment  when  not 
in    operation. 


MANAGEMENT    OF   BEAVER 


127 


Equipment,  when  not  in  use  between  seasons,  was  stored  in  a  portable 
storehouse  (Figure  48)  located  about  10  miles  above  Fort  jMohave  on 
property  owned  by  the  Arizona  Game  Department. 

Marketing: 

The  marketing  of  pelts  for  the  two  seasons  of  1943-44  and  1944-45 
was  handled  as  agreed  under  Procedure  1  by  inviting  resident  and  non- 
resident raw  fur  buyers  to  submit  competitive  sealed  bids  on  the  different 
lots  of  pelts  and  castors. 

This  plan  worked  well  the  first  season,  1943,  when  the  market  was  on 
the  uptrend  and  there  was  no  price  ceiling  established  for  this  kind  of 
beaver  skin  by  the  Office  of  Price  Administration.  Seven  buyers  of  raw 
furs  submitted  competitive  bids  and  from  the  sales  receipts  the  0.  P.  A. 
established  a  maximum  ceiling  price  of  $38.50  per  skin  for  beaver  taken 
between  Boulder  Dam  and  Mexico. 


Figure  49.  Method  of  drying  beaver  pelts  on  adjust- 
able circular  hoops  used  for  the  purpose  of  keeping  skins 
uniform  in  shape. 

At  the  1944  sale  there  were  nine  buyers  bidding.  Indications  were 
that  the  entire  group  had  mutually  agreed  not  to  bid  over  a  certain 
amount  and  later  to  portion  the  lots  accordingly,  resulting  in  an  offer  of 
only  $17.09  per  pelt.  This  offer  was  rejected  by  the  game  departments  and 
after  much  discussion,  the  offer  was  increased  to  $23.01  ])er  skin.  This 
later  offer  was  accepted  even  though  not  favorable  in  view  of  the  ceiling 
price  established  the  previous  season. 

During  the  seasons  of  1945-46  and  1946-47  the  marketing  was 
handled  under  Procedure  2  by  shipping  the  pelts  direct  to  one  of  the 


128 


CALIFORNIA    FISH    AND    OAME 


larger  fur  auction  houses  to  be  sold  at  their  discretion.  By  this  time  there 
was  a  decided  slump  in  the  fur  market,  yet  an  increase  of  $8.23  per  pelt 
was  realized  above  the  previous  season's  average  ($23.01)  at  the  peak 
of  the  fur  market. 

The  usual  method  of  grading  beaver  pelts  is  based  on  several  factors : 
care  in  preparation  of  the  pelt;  damage  to  pelt  prior  to  preparation; 
quality  of  fur  as  to  texture,  color,  density,  and  size,  according  to  the 
accompanying  scale : 

Classification  Size  Condition 

Blankets 65"  or  more  #1 — Excellent 

Extra  large 00"-64"  #2— Good 

Large 55"-59"  #3— Fair 

Medium 50"-54"  #4 — Poor 

Small 45"-49" 

Kits 44"  or  smaller 

Table  2  presents  a  recapitulation  of  the  sales  of  pelts,  castors,  and 
disbursements  of  the  sales  receipts  of  the  four  seasons.  Table  3  illustrates 
a  sample  of  the  variations  in  grades  and  average  prices  as  received  for 
the  1945-46  season.  The  importance  of  handling  and  preparing  pelts  for 

TABLE  2 
Average  Sales  Receipts 


Season 

Number  of 
pelts 

Sale  receipts 
of  pelts 

Average  price 
per  pelt 

Sale  receipts 
of  castors 

Total 
receipts 

1943-44 

68 
710 
181 

50 

$2,082  16 

16,337  92 

5,655  50 

602  25 

$30  62 
23  01 
31  24 
12  04 

$47  60 

370  47 

81  45 

15  66 

$2  129  60 

1944-45 

10  708  39 

1945-46._.. 

5,736  95 

1946-47 

617  91 

Totals... 

1,009 

$24,677  83 

$24  22 

$515  18 

$25,192  85 

Total  gross  receipts. $25,192  85 

Totalcost  of  operations... 12,060  89 

Net  profits 13,131  96 

50  Percent  net  receipts,  California...  6,565  98 

50  Percent  net  receipts,  Arizona 6,565  98 


TABLE  3 
Grade  Analysis 


Number 
of  pelts 

Grade 
number 

Grade 

Average  prices 
received 

Total 
receipts 

32 

1 

1 
1 
1 
1 
2 
3 
4 
3 
4 
3 
4 
3  and  4 

Blankets 

$47'00 
39  00 
31  00 
23  00 
19  00 

11  00 
16  75 

13  75 

14  75 
9  75 

12  75 
8  75 
6  75 

$1,504  00 

68 

Extra  large .       ...     .. .  . . 

2,652  00 

19 

Large ' 

589  00 

10 

Large  medium 

230  00 

8 

Medium ,  .       ... 

152  00 

10 

Small 

110  00 

6 

Blankets 

83  75 

6 

Blankets 

08  75 

0 

Extra  large... 

132  75 

5 

Extra  large.     

48  75 

3 

Large 

38  25 

2 

Large ,       .  . 

17  50 

6 

Medium  and  small 

28  75 

Average 

181 

31  24 

$5,655  50 

Castors,  4  cents  per  pound .. 

81  45 

$5,736  95 

MANAGEMENT    OF    BEAVER 


129 


market  was  given  considerable  attention  which  is  evident  from  the  figures 
presented  in  Table  3  (see  grade  numbers)  but  lost  in  the  average  prices 
as  presented  in  Table  2. 

Disease  Study 

During  the  month  of  January,  1945,  a  total  of  35  beaver,  17  female 
and  18  male,  of  all  ages  were  examined  for  disease  by  Dr.  Carlton  M. 
Herman,  Parasitologist,  of  the  California  Division  of  Fish  and  Game 
Disease  Laboratory. 

The  examinations  showed  that  27  of  the  35  animals  examined,  or  77 
percent,  were  parasitized  internally  by  paramphistome  flukes  (Stichorchis 
suhiriqnetus)  in  the  cecum.  This  is  probably  the  most  common  parasite 
of  beaver  and  is  found  throughout  the  beaver  range.  Many  were  infested 
with  parasitic  beetles  (Platypsylla  castoris)  which  are  found  on  the  skin 
and  in  the  fur.  No  gross  evidence  of  tularemia  was  found.  None  of  the 
animals  examined  showed  any  eA'idence  of  being  in  poor  or  unhealthy 
condition.  Most  of  those  found  infected  with  paramphistome  flukes  had 
less  than  10  worms ;  one  had  394.  No  evidence  of  embryos  was  found  in 
any  of  the  females  examined. 

Table  4  shows  the  incidence  of  cecal  flukes  (Stichorchis  suhtriquetus) 
by  age  class  of  the  35  animals  examined. 

TABLE  4 
Incidence  of  Cecal  Flukes  by  Age  Classes 


Estimated  age 

Sex 

Numbers 
examined 

Positive 

Percent 

Negative 

1  year _.            _         

Females 

Males 

4 
5 

1 

50 

80 

9 

1  year 

1 

Both 

Female.  . 

Total  1  vear 

9 

1 

1 

6 

66.6 

0 
0 

3 

2  years 

1 

2  years 

Male 

1 

Both 

Total  2  years. 

2 

12 
12 

0- 

11 
10 

0 

91.6 
83.3 

2 

A.dult 

Females 

Males 

1 

Adult 

2 

Both 

Total  .\dults.. 

24 
35 

21 
27 

87.5 
77.1 

3 

Totals 

8 

Weights  and  Measurements 

During  the  1946  season's  trapping  activities  10  fully  adult  beaver, 
consisting  of  five  males  and  five  females,  were  selected  as  a  representative 
sample  from  40  trapped  specimens  and  the  skulls  presented  to  the  Univer- 
sity of  California  Museum  of  Vertebrate  Zoology  at  Berkeley,  California. 
Before  submission  to  the  museum,  records  were  taken  of  the  weights  and 
measurements.  These  are  summarized  in  Table  5. 


Summary  and  Conclusion 

This  study,  a  cooperative  beaver  management  experiment  b}-  llie 
States  of  California  and  Arizona  for  that  portion  of  the  Colorado  River 


130 


CALIFORNIA   FISH   AND    GAME 


coustitnting  a  common  boundary  between  the  states,  was  made  to  secure 
as  much  information  as  possible  on  methods  for  the  development  of 
management  plans  which  might  be  applicable  here  or  in  other  parts  of 
either  state.  Surveys  were  made  each  year  to  determine  the  density  of  the 
population  and  to  evaluate  the  effects  of  cropping.  Harvesting  beaver  on 
a  per  pelt  basis  proved  more  satisfactory  than  on  a  basis  of  salaried 
trappers.  Equipment  purchased  by  the  states  made  it  possible  to  maintain 
a  higher  efficiency  in  the  trapping  activity  by  reducing  the  loss  in  trapped 
animals  and  damage  to  pelts.  Systematic  trapping  requires  close  super- 
vision or  the  animals  will  not  be  cropped  to  the  best  advantage  or  in  the 
predetermined  numbers. 

This  program  was  carried  on  during  the  period  1943-1947  inclusive. 
Total  costs  of  operation  (except  administrative  costs)  for  the  four  seasons 
Avas  $12,060.89.  Total  gross  receipts  for  the  four  seasons'  sale  of  1,009 
beaver  pelts  was  $25,192.85  of  which  $13,131.96  was  net  profit  divided 

TABLE  5 


Beaver  We 

ights  and 

Measurements'^ 

Sex 

Weight  in 
pounds 

Total 

length  in 

inches 

Tail  length 
in  inches 

Hind  foot 

length  in 

inches 

Ear  notch 

length  in 

inches 

Male                                                

56 
56 
*53 
41 
36 

45 

48^ 
45Ji 
44 
43^8 

10^ 
12M 

12 

74 

t 

1^6 

Male-          .                    .           

m 

Male 

IH 

Male                                                              -     . 

11/2 

Male            .                         .          

\H 

Totals                                            ..     

242 
48.40 

59 
59 
48 
t46 
43 

226}.^ 
45.30 

49 

47M 
i2H 
41J4 

43  H 

57H 
11.50 

13 
12^ 

11'/^ 

n% 

3.5 

* 

-6Ji 
6Vs 

'i{6 

Average..     ..       .       . .  

1.46 

Female        

VA 

Female. 

Female 

lJl6 

Female.          .                                     .  . 

13-2 

Female 

IH 

Totals .      

255 
51 

497 

49.6 

224M 
44.85 

450M 
45.09 

61  h' 
12.23 

118^ 

11.86 

6.93 

695-8 

6.94 

VAi 

Average .. . 

1.49 

Total  all .               ...     . 

14?i 

Average  all 

1.48 

1  Beaver  taken  on  the  Colorado  River  between  Milpitas  Wash   (Arroyo  Seco)  and  the  head  of  the  Imperial 
National  Wildlifi'  Itcfiige  on  February  1  and  2,  194G. 
*  4  pounds  deducted  (damp). 
t  2  pounds  deducted  (damp). 

equally  between  the  two  states.  Some  evidence  of  beaver  poaching  wa? 
found,  but  the  degree  of  frequency  and  extent  was  not  determined. 

The  marketing  of  pelts  through  the  fur  auction  exchange  system  was 
found  more  profitable  economically  and  more  convenient  than  tlie  method 
of  requesting  resident  raw  fur  buyers  to  submit  competitive  sealed  bids. 
Because  of  their  lower  quality  in  color  and  fur  density  there  is  less 
demand  by  the  fur  industry  for  pelts,  from  this  area  than  for  those  from 
other  parts  of  either  state. 

At  no  time  during  the  study  were  any  beaver  dams  found  in  the  river 
proper.  The  beaver  in  those  portions  of  the  river  near  Blythe,  California, 
and  near  Imperial  and  TjMguna  Dams  above  Yuma,  Arizona,  are  for  the 
most  part  considered  nuisance  beaver  because  of  agricultural  activities 


MANAGEMENT   OF   BEAVEK  131 

requiring-  diversion  of  water  for  irrigation  through  diversion  ditches, 
Avliieh  the  animals  frequently  block. 

In  general  the  animals  were  found  to  be  in  good  condition  with  no 
evidence  of  disease. 

This  paper  presents  preliminary  data  obtained  thus  far  in  this  study. 
No  attempt  has  been  made  to  draw  conclusions  or  predict  results  from 
the  data  obtained  to  date.  The  authors  feel  that  the  study  should  be  con- 
tinued over  a  greater  number  of  seasons  and  theories  further  tested  before 
reliable  predictions  and  a  sound  management  program  can  be  presented. 

The  fact  that  this  program  has  been  more  than  self  sustaining,  yield- 
ing a  substantial  profit  credited  to  the  participating  states,  justifies  con- 
tinuance of  the  management  study. 


NOTES 

SOME  NEW  AND  UNUSUAL  FISHES  FROM 
SOUTHERN  CALIFORNIA 

The  following  is  a  list  of  fishes  whose  appearance  off  the  coast  of 
Southern  California  are  unusual  enough  to  warrant  a  published  record. 
This  list  includes  specimens  received  at  the  California  State  Fisheries 
Laboratory  since  those  reported  by  Fitch,  in  "California  Fish  and 
Game,"  Vol.  33,  No.  3,  pp.  191-192,  July  1947. 

Icticus  ischanus  (Jordan  and  Thompson)  Blackrag 

An  18-inch  blackrag  was  taken  in  a  bait  net  haul  near  the  Newport 
Beach  Pier,  Orange  County,  on  September  23,  1946.  Mr.  Emery  S. 
(Casey)  Jones,  skipper  of  the  baitboat,  did  not  recognize  his  catch  and 
sent  it  to  the  California  State  Fisheries  Laboratory  for  identification. 
Until  the  specimen  was  examined  by  Dr.  Carl  L.  Hubbs  of  the  Scripps 
Institution  of  Oceanography  at  La  Jolla,  California,  and  Mr.  Wilbur  I. 
Follett  of  the  California  Academy  of  Sciences,  San  Francisco,  identifica- 
tion was  not  positive.  This  is  the  second  known  specimen  of  Icticits 
ischanus.  The  first  was  taken  at  Okinawa  in  1911  and  reported  by  Jordan 
and  Thompson  in  Mem.  Carnegie  Mus.,  6  (4),  1914 ;  242-243,  pi.  27,  fig.  4. 
Hubbs  and  Follett  will  publish  on  the  present  specimen  in  detail  at  some 
future  date.  The  crew  of  the  boat  which  caught  this  fish  stated  that  as  it 
lay  on  the  deck,  it  went  through  color  changes  comparable  to  those  noticed 
in  a  dolphin  when  removed  from  the  water.  The  final  change  was  to  an 
overall  dull  black  which  remained  in  death. 

Nautichthys  oculo-fasciatus   (Girard)   Sculpin 

A  small  sculpin  of  this  species  was  taken  on  hook  and  line  September 
14,  1947,  off  Point  Sal,  San  Luis  Obispo  County,  by  Mr.  Earl  Farris  of 


2  3         4 

INCHES 


Figure  50.     Monterey  Spanish  Mackerel,  Scomberoynorus  concolor.  Photograph 
by  Al  Johns  for  Haden  and  Carpenter,  San  Pedro 

(133) 


13-lr  CALIFORNIA    FISH    AND    GAME 

the  sport  fishing  boat  "Alaskan,"  operating  out  of  Avila.  Bolin  states 
(A  review  of  the  marine  cottid  fishes  of  California,  Stanford  Ichthvo- 
logieal  Bnlletin,  Vol.  3,  No.  1,  pp.  102-104,  fig.  40,  October,  1944)  "The 
species  ranges  from  about  Sitka,  Alaska  to  Monterey  Bay,  California  .  .  . 
although  common  in  Puget  Sound,  this  fish  is  rarely  taken  in  California. " 
The  specimen  recorded  here  represents,  therefore,  a  southern  extension 
of  the  known  range  by  approximately  125  miles. 

Scomberomorus  concolor  (Lockington)  Monterey  Spanish  Mackerel 

A  specimen  nearly  two  feet  in  length  was  taken  in  a  bait  net  on  Sep- 
tember 16,  1947,  by  the  fishing  boat  "Manhattan,"  one-half  mile  east  of 
the  Redondo  Breakwater  in  Santa  Monica  Bay.  Mr.  R.  C.  Wilson  of  the 
California  State  Fisheries  Laboratory,  who  was  aboard  the  baitboat  at 
the  time,  and  brought  the  fish  to  the  laboratory,  said  it  looked  like  a  large 
bonito  swimming  in  the  net  and  not  until  it  was  removed  from  the  net 
did  he  realize  it  was  anything  unusual.  The  Monterey  Spanish  mackerel 
is  nearly  identical  in  appearance  to  the  sierra  of  the  Mexican  Coast. 
However,  the  numerous  gold  spots  on  the  sides  of  the  sierra  are  usually 
enough  to  differentiate  the  two  species.  Scomheromorus  concolor  was 
fairly  abundant  each  fall  in  Monterey  Bay,  in  the  1870 's  and  1880 's, 
where  it  became  an  important  commercial  fish.  Around  1890,  it  failed  to 
return  in  the  fall  and  no  fish  of  this  species  was  taken  until  nearly  40 
years  later,  w^hen  one  was  recorded  from  a  San  Pedro  fish  market  in  1927. 
Since  1927,  two  were  landed  at  Monterey  in  1931,  one  at  Long  Beach  in 
1937,  and  another  in  1989.  The  most  recent  specimen  is  therefore  the  sixth 
recorded  since  thej^  disappeared  nearly  60  years  ago.  Apparently,  some- 
where in  the  Pacific  Ocean,  there  is  enough  of  a  stock  of  these  fish  to  keep 
the  species  in  existence.  It  has  been  previously  reported  in  "California 
Fish  and  Game,"  by  the  following  authors :  Roedel,  Vol.  25,  p.  343,  1939  ; 
Croker,  Vol.  23,  pp.  245-246,  1937;  Phillips,  Vol.  18,  p.  99,  1932;  and 
Starks,  Vol.  4,  p.  121,  1918. 


I     INCH 


FiGLKE   51.     Thread    Herring,    Opisthonema    libertate.    Photograph    by 
Al  Johns  for  Vernon  M.  Haden,  San  Pedro 

Opisthonema  libertate  (Gunther)  Thread  Herring 

Several  thread  herring  have  been  taken  in  bait  nets  throughout  the 
year.  The  most  recent  instance  was  one  specimen  caught  just  outside  the 


NOTES  135 

San  Pedro  breakwater  in  February,  1948.  This  interesting  fish  is  a  mem- 
ber of  the  herring  family  (Clupeidae)  and  schools  of  them  are  numerous 
from  the  region  of  Magdalena  Bay,  Lower  California,  southward  at  least 
to  Panama.  In  the  region  of  the  Gulf  of  California,  great  schools  of  thread 
herring  are  present  and  they  are  sometimes  used  as  bait  by  the  tuna  boats, 
some  of  which  do  not  empty  their  bait  tanks  until  they  near  their  home 
port  of  San  Diego  or  San  Pedro.  This  fact  has  been  offered  as  a  plausible 
explanation  of  the  occurrence  of  this  species  so  far  from  its  home  range. 
However,  it  is  possible  that  a  few  fish  do  stray  as  far  north  as  Southern 
California. 

Typhlogobius  calif orniensis  (Steindachner)  Blind  Goby 

Xot  only  Avas  the  method  of  capture  of  these  specimens  unic|ue,  but 
the  northern  range  of  the  species  was  extended  by  nearly  a  hundred  miles. 
They  were  taken  in  considerably  deeper  water  than  any  previously 
recorded,  and  the  gobies  themselves  were  all  a  great  deal  larger  than 
those  usually  collected. 

In  a  routine  check  of  an  area  after  detonation  of  a  40-pound  charge 
of  explosives  just  off  the  western  tip  of  Santa  Cruz  Island  on  February 
16,  1948,  numerous  blind  gobies  were  left  floating  on  the  surface  of  the 
water.  Gulls  picked  up  most  of  these  but  nine  specimens  were  salvaged  for 
later  examination  and  identification.  These  gobies  were  all  approximately 
three  inches  in  length  and  quite  heavy  bodied.  As  is  typical  of  this  species, 
they  were  scaleless  and  had  an  overall  pinkish  color  in  life.  The  eyes  of 
the  adults  of  this  form  are  rudimentary. 

Previously  Typhlogo'bws  calif  orniensis  has  been  collected  "only  in 
the  zone  exposed  by  low  tides  in  rocky  areas  of  our  coast.  It  usually  lives 
in  holes  in  these  rocks  in  company  with  the  ghost  shrimp,  Callianassa. 
Those  picked  up  off  Santa  Cruz  Island  were  in  water  that  varied  from 
15  to  25  feet  in  depth  and  presumably  would  have  been  more  or  less 
exposed  since  they  were  affected  by  the  blast.  Previous  recorded  range 
of  this  species  was  from  Cedros  Island,  Lower  California  to  Point  Vin- 
cente  near  San  Pedro,  California.^ — John  E.  Fitch,  Bureau  of  Marine 
Fisheries,  California  Division  of  Fish  and  Game,  March,  1948. 

HERMAPHRODITISM  IN  CHINESE  RING-NECKED  PHEASANT 

^lale  secondary  sexual  characteristics  have  been  known  to  occur  in 
the  female  pheasant  Phasianus  colchicus.  Variations  in  these  birds  range 
from  a  suggestion  of  the  white  collar  to  an  almost  complete  duplication 
of  male  plumage  with  a  dark  greenish,  black  head,  red  side  of  head,  white 
collar,  grey-green  saddle,  and  dark  brown  body  feathers.  Rudimentary 
spurs  haA'e  been  noted.  However,  the  tail  feathers  are  shorter,  and  the 
general  structure  of  the  birds  are  typical  of  the  smaller  female.  Internal 
examination  of  such  individuals  reveals  ovaries  that  are  atrophied. 

During  the  past  pheasant  season  opportunity  was  afforded  the 
author  to  examine  many  of  the  pheasants  taken  by  hunters.  Among  the 
birds  autopsied  one  small  pheasant  possessed  plumage  more  completely 
characteristic  of  a  male  than  any  aberrant  female  that  had  been  seen 
previously.  Small  spurs  were  present.  The  ovaries  and  oviduct  were  noted 
on  the  left  side.  Anterior  to  the  ovaries  were  the  ellipsoidal  testes,  and 
leading  from  them  were  the  bilateral  vas  deferens. 


136  CALIFORNIA    FISH    AND    GAME 

This  apparent  hermaphrodite  had  an  abundance  of  body  fat  and  its 
ovaries  were  not  atrophied.  Although  visual  inspeetion  of  the  body  cavity 
and  internal  organs  was  permitted,  opportunity  to  collect  the  gonads  for 
further  study  was  not  possible. — Merton  N.  Rosen;  Bureau  of  Game  Con- 
servation; California  Division  of  Fish  and  Game;  March,  1947. 

RESIGNATION  OF  COMMISSION  PRESIDENT,  H.  H.  ARNOLD 

RESOLUTION 

"Whereas.  For  the  past  two  years  General  H.  H.  Arnold  has  faith- 
fully served  the  public,  the  State  of  California  and  the  Fish  and  Game 
Commission  as  an  honored  member  and  president ;  and 

Whereas,  The  principles  of  conservation  and  preservation  of  Cali- 
fornia fish  and  game,  and  the  public 's  interest  therein,  have  been  stimu- 
lated and  enhanced  during  General  Arnold 's  term  of  office ;  and 

Whereas,  This  commission  desires  to  express  to  General  Arnold  its 
appreciation  and  thanks  for  his  inspirational  effort  and  continuing  guid- 
ance in  its  behalf  and  in  behalf  of  the  conservation  of  wildlife  in  Califor- 
nia, and  also  desires  to  acquaint  the  public  at  large  and  the  Governor  of 
this  State  of  such  expression ;  now,  therefore,  be  it 

Resolved,  hy  the  Fish  and  Game  Commission  of  the  State  of  Califor- 
nia, in  regular  meeting  assembled,  That  its  regret  to  expressed  to  General 
Arnold  for  the  necessity  of  tendering  his  resignation ;  and  further 

Resolved,  That  its  thanks  and  appreciation  be  and  hereby  are 
expressed  publicly  to  General  H.  H.  Arnold  for  his  interest,  time,  and 
effort  during  the  past  two  years  in  behalf  of  this  commission  as  an 
honored  member  and  president ;  and  further 

Resolved,  That  copies  of  this  resolution  be  forwarded  to  the  Governor 
of  the  State  of  California  and  to  General  H.  H.  Arnold,  and  that  addi- 
tional copies  hereof  be  released  to  the  press  and  published  in  all  magazines 
and  journals  published  by  this  commission.  Adopted  April  30, 1948. 

APPOINTMENT  OF  COMMISSIONER  E.  L.  CARTY 

Edwin  L.  Cartj^,  Mayor  of  Oxnard,  was  appointed  to  the  Fish  and 
Game  Commission  by  Governor  Warren  to  fill  the  unexpired  term  of 
General  H.  H.  Arnold  who  resigned  on  account  of  ill  health.  Mr.  Carty 
formerly  served  a  full  term  as  commissioner,  being  appointed  by  Governor 
Olson,  to  the  first  five-man  commission  created  by  vote  of  the  people. 
Sportsmen  and  personnel  will  remember  Mr.  Carty  for  the  building  of 
the  Fillmore  Hatchery,  as  well  as  his  other  efforts  for  better  hunting  and 
fishing  in  California. 

RESIGNATION  OF  EMIL  J.  N.  OTT,  JR.,  AS  EXECUTIVE 

OFFICER 

The  resignation  of  Emil  J.  N.  Ott,  Jr.,  Executive  Officer,  effective 
April  30th,  was  accepted  by  the  commission  with  regrets  and  an  expres- 
sion of  goodwill  in  whatever  enterprise  witli  which  he  becomes  asso- 
ciated. Mr.  Ott  had  official  capacitj^  with  the  division  for  about  three  and 
a  lialf  years  and  was  very  energetic  in  all  his  endeavors. 

APPOINTMENT  OF  E.  L.  MACAULAY  AS  EXECUTIVE  OFFICER 

Effective  May  11th,  E.  L.  Macaulay  became  the  Executive  Officer  of 
the  division.  Prior  to  the  appointment  Mr.  Macaulay  had  been  Chief, 
Bureau  of  Patrol,  for  19  years.  He  served  in  the  U.  S.  Army  during  both 
world  wars  with  credit  to  himself  and  his  branch  of  the  service. 


REPORTS 

FISH   CASES 
January,  February,  March,  1948 


Offense 


Number 
arrests 


Fines 


JaU 
sentences 

fdays) 


Abalone:  Undersize,  overlimit,  no  license,  possession,  closed  season,  failure  to 

show  license,  out  of  shell - 

Angling:  Use  of  another's  license,  no  license,  transfer  of  license,  set  lines,  closed 
season,  failure  to  show  Ucense,  spear  within  300  feet  of  stream,  use  of  ex- 
plosives, operating  wire  fish  trap,  nonresident  using  resident  license,  false 

statement  to  secure  license 

Bass:  Late  and  early  fishing,  more  than  one  line,  undersize,  seining,  night  fishing, 

no  license,  other  than  angling. 

Bluegill:  Closed  season 

Catfish :  Seining,  selling  undersize,  undersize,  night  fishing 

Clams:  Transfer  of  license,  undersize,  night  clamming,  out  of  shell,  illegal  hours, 

no  h'jeisc-- 

Crabs:  Undersize 

Crappie:  Closed  season,  seining 

Cockles:  Over  limit,  no  license . 

Commercial:  No  license,  wastage  of  fish,  failure  to  render  reports,  buying  with- 
out giving  receipt,  failure  to  show  license  on  demand 

Lobsters:  l^ndersize,  illegal  use  of  traps,  oversize,  no  boat  registration 

Pollution:  Oil,  sawdust,  edgings,  tannic  acid,  fish  refuse 

Salmon:  Spearing  in  spawning  area,  snagging 

Sunfish:  Closed  season,  netting 

Trout:  Closed  season,  possession  spear,  night  fishing,  over  limit,  other  than 

angling,  snagging,  more  than  one  rod,  no  license 

Mackerel  sardines :  Delivering  and  receiving  undersize 

Court  forfeitures:  Undersize  mackerel  and  sardines 


124 


255 

61 
6 


200 

3 

8 

33 

35 

18 

19 

2 

4 

15 
25 


$2,917  00 


5,062  00 

1,266  00 

82  00 

55  00 

4,813  00 

75  00 

150  00 

665  00 

810  00 

970  00 

2,225  00 

40  00 

92  50 

365  00 

190  00 

6,412  00 


Totals. 


980 


$26,189  50 


30H 


il'A 


72 


GAME   CASES 
January,  February,  March,  1948 


Offense 


Number 
arrests 


Fines 


Jail 

sentences 

(days) 


Coots:  Closed  season,  no  license,  shooting  from  car 

Deer:  Possession  doe,  closed  season,  possession  spike  buck,  spotlighting 

Deer  meat:  Possession  closed  season 

Deer  tags:  Failure  to  validate ... .. 

Doves:  Closed  season,  unplugged  gun,  over  limit 

Du'ki:  Early  and  late  shooting,  over  limit,  shooting  from  power  boat,  no  stamp, 

rifle,  closed  season,  possession  for  sale 

Frogs:  Closed  season 

Geese:  Late  shooting,  over  limit,  closed  season,  using  live  decoy,  selling 

Hunting:  Unplugged  gun,  early  and  late  shooting,  no  license,  transfering  license, 

night  hunting,  spotlighting,  failure  to  show  license  on  demand,  no  alien  license 

Non  game:  Killing  robins,  meadow  larks,  thrush 

Pheasants:  Possession  hen,  closed  season,  rifle,  overlimit 

Pigeons:  No  license,  over  limit,  closed  season,  taking  homing  pigeon 

Quail:  Unplugged  gun,  overlimit 

Rabbits:  Closed  season,  night  hunting 

Shore  birds:  Passession  seagulls,. killdeer 

Swans:  Possession,  killing,  attempt  to  take 

Trespass:  Water  fowl  management  area ._ 

Trapping :  Removing  animals  from  State  trapper's  trap 

Elk  meat:  Possession  closed  season 

Totals 


17 
50 
27 
5 
19 

221 

1 

34 

346 
10 
40 

7 

13 
39 

5 
17 
19 

3 

1 


$385  00 

8,413  00 

3,325  00 

50  00 

443  00 

9,435  00 

25  00 

835  00 

4.919  00 
325  00 

2,555  00 
160  00 
350  00 
873  00 
120  00 
655  00 
380  00 
120  00 
50  00 


526 
120 


30 


14.4 


S74 


S33,418  00 


690^ 


(137) 


138  CALIFORNIA    FISH    AND    GAME 

SEIZURES  OF   FISH    AND   GAME 
January,  February,  March,  1948 

Fish: 

Al  wlones 1,354 

Ahalones,  pounds 2,060 

Striped  bass 30 

Black  bass 4 

Carp . 7 

Catfish 49 

Catfish,  pounds 19 

Crab 42 

Crappie 10 

Coclcles : 10,045 

Clams 4,S21 

BlucgiU 11 

Bluegill,  pounds 30 

Lobsters 50 

Lohtters,  pounds 1,195 

Salmon r 2 

Skipjack,  pounds 7,680 

Trout 26 

Trout,  pounds 20 

Mackerel  and  sardines 512,425 

Game; 

Coots 13 

Deer 20 

Deer  meat,  pounds 602 

Doves 10 

Ducks 623 

Frogs - 14 

Geese 52 

Non  game 22 

Pheasants 41 

Pigeons 2 

Quail 4 

Rabbits -..  20 

Shore  birds ; 17 

Swans 12 


89K00      4-48      5500